Taking and Importing Marine Mammals; U.S. Navy Training in the Southern California Range Complex, 3882-3918 [E9-1073]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 216
[Docket No. 0808061069–81583–02]
RIN 0648–AW91
Taking and Importing Marine
Mammals; U.S. Navy Training in the
Southern California Range Complex
AGENCY: National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Final rule.
NMFS, upon application from
the U.S. Navy (Navy), is issuing
regulations to govern the unintentional
taking of marine mammals incidental to
training, maintenance, and research,
development, testing and evaluation
(RDT&E) activities conducted in the
Southern California Range Complex
(SOCAL Range Complex), which
extends south and southwest off the
southern California coast, for the period
of January 2009 through January 2014.
The Navy’s activities are considered
military readiness activities pursuant to
the Marine Mammal Protection Act
(MMPA), as amended by the National
Defense Authorization Act for Fiscal
Year 2004 (NDAA). These regulations,
which allow for the issuance of ‘‘Letters
of Authorization’’ (LOAs) for the
incidental take of marine mammals
during the described activities and
specified timeframes, prescribe the
permissible methods of taking and other
means of affecting the least practicable
adverse impact on marine mammal
species and their habitat, as well as
requirements pertaining to the
monitoring and reporting of such taking.
DATES: Effective January 14, 2009
through January 14, 2014.
ADDRESSES: A copy of the Navy’s
application (which contains a list of the
references used in this document),
NMFS’ Record of Decision (ROD), and
other documents cited herein, may be
obtained by writing to Michael Payne,
Chief, Permits, Conservation and
Education Division, Office of Protected
Resources, National Marine Fisheries
Service, 1315 East-West Highway, Silver
Spring, MD 20910–3225 or by telephone
via the contact listed here (see FOR
FURTHER INFORMATION CONTACT).
FOR FURTHER INFORMATION CONTACT: Jolie
Harrison, Office of Protected Resources,
NMFS, (301) 713–2289, ext. 166.
SUPPLEMENTARY INFORMATION: Extensive
supplementary information was
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SUMMARY:
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provided in the proposed rule for this
activity, which was published in the
Federal Register on Tuesday, October
14, 2008 (73 FR 60836). This
information will not be reprinted here
in its entirety; rather, all sections from
the proposed rule will be represented
herein and will contain either a
summary of the material presented in
the proposed rule or a note referencing
the page(s) in the proposed rule where
the information may be found. Any
information that has changed since the
proposed rule was published will be
addressed herein. Additionally, this
final rule contains a section that
responds to the comments received
during the public comment period.
Background
Sections 101(a)(5)(A) and (D) of the
MMPA (16 U.S.C. 1361 et seq.) direct
the Secretary of Commerce (Secretary)
to allow, upon request, the incidental,
but not intentional taking of marine
mammals by U.S. citizens who engage
in a specified activity (other than
commercial fishing) during periods of
not more than five consecutive years
each if certain findings are made and
regulations are issued or, if the taking is
limited to harassment and of no more
than 1 year, the Secretary shall issue a
notice of proposed authorization for
public review.
Authorization shall be granted if
NMFS finds that the taking will have a
negligible impact on the species or
stock(s), will not have an unmitigable
adverse impact on the availability of the
species or stock(s) for subsistence uses,
and if the permissible methods of taking
and requirements pertaining to the
mitigation, monitoring and reporting of
such taking are set forth.
NMFS has defined ‘‘negligible
impact’’ in 50 CFR 216.103 as:
An impact resulting from the specified
activity that cannot be reasonably expected
to, and is not reasonably likely to, adversely
affect the species or stock through effects on
annual rates of recruitment or survival.
The NDAA (Pub. L. 108–136)
removed the ‘‘small numbers’’ and
‘‘specified geographical region’’
limitations and amended the definition
of ‘‘harassment’’ as it applies to a
‘‘military readiness activity’’ to read as
follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the
significant potential to injure a marine
mammal or marine mammal stock in the wild
[Level A Harassment]; or
(ii) Any act that disturbs or is likely to
disturb a marine mammal or marine mammal
stock in the wild by causing disruption of
natural behavioral patterns, including, but
not limited to, migration, surfacing, nursing,
breeding, feeding, or sheltering, to a point
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where such behavioral patterns are
abandoned or significantly altered [Level B
Harassment].
Summary of Request
On April 1, 2008, NMFS received an
application from the Navy requesting
authorization for the take of individuals
of 37 species of marine mammals
incidental to upcoming Navy training
activities, maintenance, and research,
development, testing, and evaluation
(RDT&E) activities to be conducted
within the SOCAL Range Complex,
which extends southwest approximately
600 nm in the general shape of a 200nm wide rectangle (see the Navy’s
application), over the course of 5 years.
These activities are military readiness
activities under the provisions of the
NDAA. The Navy states, and NMFS
concurs, that these military readiness
activities may incidentally take marine
mammals present within the SOCAL
Range Complex by exposing them to
sound from mid-frequency or high
frequency active sonar (MFAS/HFAS) or
underwater detonations. The Navy
requests authorization to take
individuals of 37 species of marine
mammals by Level B Harassment.
Further, though they do not anticipate it
to occur, the Navy requests
authorization to take, by injury or
mortality, up to 10 beaked whales over
the course of the 5-yr period for which
the regulations will be in effect.
Background of Navy Request
The proposed rule contains a
description of the Navy’s mission, their
responsibilities pursuant to Title 10 of
the United States Code, and the specific
purpose and need for the activities for
which they requested incidental take
authorization. The description
contained in the proposed rule has not
changed. See 73 FR 60836.
Overview of the SOCAL Range Complex
The proposed rule contains an
overview of the SOCAL Range Complex
that describes the SOCAL Operational
Areas (OPAREAS), the Special Use
Airspaces, San Clemente Island, and the
overlap with Point Mugu Sea Range for
certain anti-submarine warfare (ASW)
training. The description contained in
the proposed rule has not changed. See
73 FR 60836, page 60837.
Description of the Specified Activities
The proposed rule contains a
complete description of the Navy’s
specified activities that are covered by
these final regulations, and for which
the associated incidental take of marine
mammals will be authorized in the
related LOAs. The proposed rule
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Navy’s activities and hours of sonar
operation conducted.
The Navy is developing the Advanced
Extended Echo Ranging (AEER) system
as a replacement to the IEER system.
AEER would use a new active sonobuoy
(AN/SSQ–125) that utilizes a tonal (or a
sonar ping) vice impulsive (or
explosive) sound source as a
replacement for the SSQ–110A (the
system used in IEER). AEER will still
use the ADAR sonobuoy as the systems
receiver and be deployed by Marine
Patrol Aircraft. As AEER is introduced
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for Fleet use, IEER will be removed. The
same total number of buoys will be
deployed as were presented in the
proposed rule, but a subset of them will
be AEER instead of IEER. The small
difference in the number of anticipated
marine mammal takes that will result
from this change is indicated in the take
table, along with other minor
modifications. This small change in the
take numbers did not affect NMFS’
analysis of and conclusions regarding
the proposed action.
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describes the nature of the activities
involving both mid and high-frequency
active sonar (MFAS and HFAS) and
explosive detonations, as well as the
MFAS and HFAS sound sources and
explosive types. See 73 FR 60836, pages
60837–60847. The narrative description
of the action contained in the proposed
rule has not changed, with the
exception of the change from IEER to
AEER described in the paragraph below.
Tables 1, 2, and 3 summarize the sonar
and explosive exercise types used in the
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the abundance estimates from both the
2007 stock assessment reports and the
draft 2008 reports. This correction did
not affect NMFS analysis, as take
estimates are based on density estimates
(not abundance estimates), which
remain unchanged from those presented
in the proposed rule.
The proposed rule indicated (73 FR
60836, page 60849) that the last sighting
of a Steller sea lion in Southern
California was that of a sub adult male
that was briefly on San Miguel Island in
1998. In fact, a Steller sea lion was
sighted in Newport Harbor in April
2008 and a Steller sea lion (that may
have been the same individual) live
stranded in Santa Barbara in the
summer of 2008. This correction did not
affect NMFS analysis and, as indicated
in the proposed rule, Steller sea lions
are not likely to be present in the action
area or taken by the Navy’s specified
activities.
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Area of the Specified Activities in the
proposed rule remains unchanged (see
73 FR 60836, pages 60846–60850).
For this rulemaking and subsequent
LOA, NMFS’ Southwest Fisheries
Science Center calculated marine
mammal density estimates based on
compiled densities from vessel surveys
conducted from 1986 to 2005, and
provided it to the Navy as Government
Furnished Information (GFI). These
density estimates are included in Table
4 and remain unchanged from the
proposed rule. The proposed rule
contains a description of the methods
used to estimate density. During the
public comment period for the proposed
rule, several members of the public
noted and commented that the
abundance numbers provided for some
marine mammal species were not from
the latest NMFS stock assessment
reports. Those numbers have been
updated in Table 4, which now includes
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Description of Marine Mammals in the
Area of the Specified Activities
There are 41 marine mammal species
with possible or confirmed occurrence
in the SOCAL Range Complex. Nine
marine mammal species listed as
federally endangered under the
Endangered Species Act (ESA) can
occur in the SOCAL Range Complex:
The humpback whale, North Pacific
right whale, sei whale, fin whale, blue
whale, sperm whale, southern resident
killer whale, Guadalupe fur seal, and
Steller sea lion. The proposed rule
contains a discussion of three species
that are not considered further in the
analysis (southern resident killer whale,
North Pacific right whale, and Steller
sea lion) because of their rarity in the
SOCAL Range Complex. With the
exception of marine mammal
abundance and Steller sea lion
correction discussed below, the
Description of Marine Mammals in the
A Brief Background on Sound
The proposed rule contains a section
that provides a brief background on the
principles of sound that are frequently
referred to in this rulemaking. See 73 FR
60836, pages 60850–60851. This section
also includes a discussion of the
functional hearing ranges of the
different groups of marine mammals (by
frequency) as well as a discussion of the
two main sound metrics used in NMFS
analysis (sound pressure level (SPL) and
sound energy level (SEL)). The
information contained in the proposed
rule has not changed.
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Potential Effects of Specified Activities
on Marine Mammals
With respect to the MMPA, NMFS’
effects assessment serves four primary
purposes: (1) To prescribe the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
harassment), Level A Harassment
(injury), or mortality, including an
identification of the number and types
of take that could occur by Level A or
B harassment or mortality) and to
prescribe other means of affecting the
least practicable adverse impact on such
species or stock and its habitat (i.e.,
mitigation); (2) to determine whether
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the specified activity will have a
negligible impact on the affected species
or stocks of marine mammals (based on
the likelihood that the activity will
adversely affect the species or stock
through effects on annual rates of
recruitment or survival); (3) to
determine whether the specified activity
will have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (however,
there are no subsistence communities
that would be affected in the SOCAL
Range Complex, so this determination is
inapplicable for this rulemaking); and
(4) to prescribe requirements pertaining
to monitoring and reporting.
In the Potential Effects of Specified
Activities on Marine Mammals Section
of the proposed rule NMFS included a
qualitative discussion of the different
ways that MFAS/HFAS and underwater
explosive detonations may potentially
affect marine mammals (some of which
NMFS would not classify as
harassment). See 73 FR 60836, pages
60851–60863. Marine mammals may
experience direct physiological effects
(such as threshold shift), acoustic
masking, impaired communications,
stress responses, and behavioral
disturbance. This section also included
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a discussion of some of the suggested
explanations for the association between
the use of MFAS and marine mammal
strandings (such as behaviorallymediated bubble growth) that have been
observed a limited number of times in
certain circumstances (the specific
events are also described). See 73 FR
60836, pages 60859–60863. The
information contained in the Potential
Effects of Specified Activities on Marine
Mammals Section from the proposed
rule has not changed, with the
exception of the following sentence. On
page 60861, NMFS said ‘‘Other species
(Stenella coeruleoalba, Kogia breviceps
and Balaenoptera acutorostrata) have
stranded, but in much lower numbers
and less consistently than beaked
whales.’’ As a member of the public
pointed out, and as NMFS stated on
page 60860 of the proposed rule, there
was no likely association between the
minke whale and spotted dolphin
strandings referred to and the operation
of MFAS. Therefore, the sentence
should read ‘‘Other species, such as
Kogia breviceps, have stranded in
association with the operation of MFAS,
but in much lower numbers and less
consistently than beaked whales.’’
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Later, in the Estimated Take of Marine
Mammals section, NMFS relates and
quantifies the potential effects to marine
mammals from MFAS/HFAS and
underwater detonation of explosives
discussed here to the MMPA regulatory
definitions of Level A and Level B
Harassment. NMFS has also considered
the effects of mortality on these species.
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Mitigation
In order to issue an incidental take
authorization (ITA) under Section
101(a)(5)(A) of the MMPA, NMFS must
prescribe regulations setting forth the
‘‘permissible methods of taking
pursuant to such activity, and other
means of affecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’ The
NDAA of 2004 amended the MMPA as
it relates to military readiness activities
and the incidental take authorization
process such that ‘‘least practicable
adverse impact’’ shall include
consideration of personnel safety,
practicality of implementation, and
impact on the effectiveness of the
‘‘military readiness activity.’’ The
SOCAL Range Complex activities
described in the proposed rule are
considered military readiness activities.
NMFS reviewed the Navy’s proposed
SOCAL Range Complex activities and
the proposed SOCAL mitigation
measures (which the Navy refers to as
Protective Measures) presented in the
Navy’s application to determine
whether the activities and mitigation
measures were capable of achieving the
least practicable adverse effect on
marine mammals. NMFS determined
that further discussion was necessary
regarding the potential relationship
between the operation of MFAS/HFAS
and marine mammal strandings.
Any mitigation measure prescribed by
NMFS should be known to accomplish,
have a reasonable likelihood of
accomplishing (based on current
science), or contribute to the
accomplishment of one or more of the
general goals listed below:
(a) Avoidance or minimization of
injury or death of marine mammals
wherever possible (goals b, c, and d may
contribute to this goal).
(b) A reduction in the numbers of
marine mammals (total number or
number at biologically important time
or location) exposed to received levels
of MFAS/HFAS, underwater
detonations, or other activities expected
to result in the take of marine mammals
(this goal may contribute to a, above, or
to reducing harassment takes only).
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(c) A reduction in the number of times
(total number or number at biologically
important time or location) individuals
would be exposed to received levels of
MFAS/HFAS, underwater detonations,
or other activities expected to result in
the take of marine mammals (this goal
may contribute to a, above, or to
reducing harassment takes only).
(d) A reduction in the intensity of
exposures (either total number or
number at biologically important time
or location) to received levels of MFAS/
HFAS, underwater detonations, or other
activities expected to result in the take
of marine mammals (this goal may
contribute to a, above, or to reducing the
severity of harassment takes only).
(e) A reduction in adverse effects to
marine mammal habitat, paying special
attention to the food base, activities that
block or limit passage to or from
biologically important areas, permanent
destruction of habitat, or temporary
destruction/disturbance of habitat
during a biologically important time.
(f) For monitoring directly related to
mitigation—an increase in the
probability of detecting marine
mammals, thus allowing for more
effective implementation of the
mitigation (shut-down zone, etc.).
NMFS worked with the Navy to
identify potential additional practicable
and effective mitigation measures,
which included a careful balancing of
the likely benefit of any particular
measure to the marine mammals with
the likely effect of that measure on
personnel safety, practicality of
implementation, and impact on the
‘‘military-readiness activity’’. NMFS and
the Navy developed a Stranding
Response Plan to address the concern
listed above.
The Navy’s proposed mitigation
measures, as well as the Stranding
Response Plan, which is required under
these regulations, were described in
detail in the proposed rule (73 FR
60836, pages 60863–60870). The Navy’s
measures address personnel training,
lookout and watchstander
responsibilities, and operating
procedures for activities using both
MFAS/HFAS and explosive
detonations. Three modifications (see
below) have been made to the mitigation
measures described in the proposed
rule. The final SOCAL Stranding
Response Plan, which includes a
shutdown protocol, a stranding
investigation plan, and a requirement
for Navy and NMFS to implement an
MOA that will establish a framework
whereby the Navy can (and provide the
Navy examples of how they can best)
assist NMFS with stranding
investigations in certain circumstances,
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may be viewed at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications.
Additionally, the mitigation measures
are included in full in the codified text
of the regulations.
The proposed rule (the regulatory
text, not the preamble) contained a
measure in which the Navy indicated
that ‘‘prior to conducting the exercise,
remotely sensed sea surface temperature
maps would be reviewed. SINKEX shall
not be conducted within areas where
strong temperature discontinuities are
present, thereby indicating the existence
of oceanographic fronts.’’ See 73 FR
60836, page 60904. The Navy included
this measure in the LOA application in
error. The removal of the measure does
not change NMFS’ analysis and
therefore the measure is not included in
the final rule.
The following measure has been
added to the Mitigation section of the
regulations: Night vision goggles shall
be available to all ships and air crews
for use as appropriate.
Last, the same mitigation measures
outlined for the IEER system in the
proposed rule will also be applied to the
similar, but newly described, AEER
system.
NMFS has determined that the Navy’s
proposed mitigation measures (from the
LOA application), along with the
Stranding Response Plan (and when the
Adaptive Management (see Adaptive
Management below) component is taken
into consideration) are adequate means
of effecting the least practicable adverse
impacts on marine mammal species or
stocks and their habitat, paying
particular attention to rookeries, mating
grounds, and areas of similar
significance, while also considering
personnel safety, practicality of
implementation, and impact on the
effectiveness of the military readiness
activity. The justification for this
conclusion is discussed in the
Mitigation Conclusion section of the
proposed rule. See 73 FR 60836, pages
60870–60871. The Mitigation
Conclusion Section of the proposed rule
has not changed. Research and
Conservation Measures for Marine
Mammals.
The Navy provides a significant
amount of funding and support for
marine research. The Navy provided
$26 million in Fiscal Year 2008 and
plans for $22 million in Fiscal Year
2009 to universities, research
institutions, federal laboratories, private
companies, and independent
researchers around the world to study
marine mammals. Over the past five
years the Navy has funded over $100
million in marine mammal research.
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The U.S. Navy sponsors seventy percent
of all U.S. research concerning the
effects of human-generated sound on
marine mammals and 50 percent of such
research conducted worldwide. Major
topics of Navy-supported research
include the following:
• Better understanding of marine
species distribution and important
habitat areas,
• Developing methods to detect and
monitor marine species before and
during training,
• Understanding the effects of sound
on marine mammals, sea turtles, fish,
and birds, and
• Developing tools to model and
estimate potential effects of sound.
The Navy’s Office of Naval Research
currently coordinates six programs that
examine the marine environment and
are devoted solely to studying the
effects of noise and/or the
implementation of technology tools that
will assist the Navy in studying and
tracking marine mammals. The six
programs are as follows:
• Environmental Consequences of
Underwater Sound,
• Non-Auditory Biological Effects of
Sound on Marine Mammals,
• Effects of Sound on the Marine
Environment,
• Sensors and Models for Marine
Environmental Monitoring,
• Effects of Sound on Hearing of
Marine Animals, and
• Passive Acoustic Detection,
Classification, and Tracking of Marine
Mammals.
The Navy has also developed the
technical reports referenced within this
document and the SOCAL Range
Complex EIS, such as the Marine
Resource Assessments. Furthermore,
research cruises by NMFS and by
academic institutions have received
funding from the U.S. Navy.
The Navy has sponsored several
workshops to evaluate the current state
of knowledge and potential for future
acoustic monitoring of marine
mammals. The workshops brought
together acoustic experts and marine
biologists from the Navy and other
research organizations to present data
and information on current acoustic
monitoring research efforts and to
evaluate the potential for incorporating
similar technology and methods on
instrumented ranges. However, acoustic
detection, identification, localization,
and tracking of individual animals still
requires a significant amount of research
effort to be considered a reliable method
for marine mammal monitoring. The
Navy supports research efforts on
acoustic monitoring and will continue
to investigate the feasibility of passive
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acoustics as a potential mitigation and
monitoring tool.
Overall, the Navy will continue to
fund ongoing marine mammal research,
and is planning to coordinate long-term
monitoring/studies of marine mammals
on various established ranges and
operating areas. The Navy will continue
to research and contribute to university/
external research to improve the state of
the science regarding marine species
biology and acoustic effects. These
efforts include mitigation and
monitoring programs; data sharing with
NMFS and via the literature for research
and development efforts.
Long-Term Prospective Study
Apart from this final rule, NMFS,
with input and assistance from the Navy
and several other agencies and entities,
will perform a longitudinal
observational study of marine mammal
strandings to systematically observe and
record the types of pathologies and
diseases and investigate the relationship
with potential causal factors (e.g., sonar,
seismic surveys, weather). The proposed
rule contained an outline of the
proposed study (73 FR 60836, pages
60837–60838). No changes have been
made to the longitudinal study as
described in the proposed rule.
Monitoring
In order to issue an ITA for an
activity, Section 101(a)(5)(A) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking’’. The MMPA implementing
regulations at 50 CFR 216.104 (a)(13)
indicate that requests for LOAs must
include the suggested means of
accomplishing the necessary monitoring
and reporting that will result in
increased knowledge of the species and
of the level of taking or impacts on
populations of marine mammals that are
expected to be present.
Monitoring measures prescribed by
NMFS should accomplish one or more
of the following general goals:
(a) An increase in the probability of
detecting marine mammals, both within
the safety zone (thus allowing for more
effective implementation of the
mitigation) and in general to generate
more data to contribute to the effects
analyses.
(b) An increase in our understanding
of how many marine mammals are
likely to be exposed to levels of MFAS/
HFAS (or explosives or other stimuli)
that we associate with specific adverse
effects, such as behavioral harassment,
TTS, or PTS.
(c) An increase in our understanding
of how marine mammals respond
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(behaviorally or physiologically) to
MFAS/HFAS (at specific received
levels), explosives, or other stimuli
expected to result in take and how
anticipated adverse effects on
individuals (in different ways and to
varying degrees) may impact the
population, species, or stock
(specifically through effects on annual
rates of recruitment or survival).
(d) An increased knowledge of the
affected species.
(e) An increase in our understanding
of the effectiveness of certain mitigation
and monitoring measures.
(f) A better understanding and record
of the manner in which the authorized
entity complies with the incidental take
authorization.
Proposed Monitoring Plan for the
SOCAL Range Complex
As NMFS indicated in the proposed
rule, the Navy has (with input from
NMFS) fleshed out the details of and
made improvements to the SOCAL
Range Complex Marine Mammal and
Sea Turtle Monitoring Plan (Monitoring
Plan). Additionally, NMFS and the
Navy have incorporated a
recommendation from the public, which
recommended the Navy hold a
workshop to discuss the Navy’s
Monitoring Plan (see Monitoring
Workshop section). The final SOCAL
Range Complex Monitoring Plan, which
is summarized below may be viewed at
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications. The Navy
plans to implement all of the
components of the Monitoring Plan;
however, only the marine mammal
components (not the sea turtle
components) will be required by the
MMPA regulations and associated
LOAs.
The draft Monitoring Plan for the
SOCAL Range Complex has been
designed as a collection of focused
‘‘studies’’ (described fully in the SOCAL
Range Complex Monitoring Plan) to
gather data that will allow the Navy to
address the following questions:
(1) Are marine mammals and sea
turtles exposed to MFAS, especially at
levels associated with adverse effects
(i.e., based on NMFS’ criteria for
behavioral harassment, TTS, or PTS)? If
so, at what levels are they exposed?
(2) If marine mammals and sea turtles
are exposed to MFAS in the SOCAL
Range Complex, do they redistribute
geographically as a result of continued
exposure? If so, how long does the
redistribution last?
(3) If marine mammals and sea turtles
are exposed to MFAS, what are their
behavioral responses to various levels?
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(4) What are the behavioral responses
of marine mammals and sea turtles that
are exposed to explosives at specific
levels?
(5) Is the Navy’s suite of mitigation
measures for MFAS and explosives (e.g.,
PMAP, major exercise measures agreed
to by the Navy through permitting)
effective at avoiding TTS, injury, and
mortality of marine mammals and sea
turtles?
Data gathered in these studies will be
collected by qualified, professional
marine mammal biologists that are
experts in their field. They will use a
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combination of the following methods
to collect data:
• Visual Surveys—Vessel and aerial.
• Passive Acoustic Monitoring
(PAM), including working with the
passive acoustic detection capabilities
of Navy’s SOAR fixed range.
• Marine Mammal Observers (MMOs)
on Navy Vessels.
• Marine Mammal Tagging.
In the five proposed study designs (all
of which cover multiple years), the
above methods will be used separately
or in combination to monitor marine
mammals in different combinations
before, during, and after activities
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utilizing MFAS/HFAS or explosive
detonations. Table 5 contains a
summary of the monitoring effort that is
planned for each study in each year
(effort may vary slightly between years
or study type, but overall effort will
remain constant). The SOCAL Range
Complex Monitoring Plan is designed to
collect data on all marine mammals and
sea turtles encountered during
monitoring studies. However, priority
will be given to ESA-listed species and
taxa in which MFAS exposure, under
certain circumstances and strandings
have been linked (beaked whales and
other deep-diving species).
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Monitoring Workshop
During the public comment period on
the SOCAL Range Complex proposed
rule (as well as the Hawaii Range
Complex proposed rule), NMFS
received a comment which, in
consultation with the Navy, we have
chosen to incorporate into the final rule
(in a modified form). One commenter
recommended that a workshop or panel
be convened to solicit input on the
monitoring plan from researchers,
experts, and other interested parties.
The SOCAL Range Complex proposed
rule included an adaptive management
component and both NMFS and the
Navy believe that a workshop would
provide a means for Navy and NMFS to
consider input from participants in
determining whether or how to modify
monitoring techniques to more
effectively accomplish the goals of
monitoring set forth earlier in the
document. NMFS and the Navy believe
that this workshop concept is valuable
in relation to all of the Range Complexes
and major training exercise rules and
LOAs that NMFS is working on with the
Navy at this time, and consequently this
single Monitoring Workshop will be
included as a component of all of the
rules and LOAs that NMFS will be
processing for the Navy in the next year
or so.
The Navy, with guidance and support
from NMFS, will convene a Monitoring
Workshop, including marine mammal
and acoustic experts as well as other
interested parties, in 2011. The
Monitoring Workshop participants will
review the monitoring results from the
previous two years of monitoring
pursuant to the SOCAL Range Complex
rule as well as monitoring results from
other Navy rules and LOAs (e.g., the
Atlantic Fleet Active Sonar Training,
Hawaii Range Complex (HRC), and
other rules). The Monitoring Workshop
participants would provide their
individual recommendations to the
Navy and NMFS on the monitoring
plan(s) after also considering the current
science (including Navy research and
development) and working within the
framework of available resources and
feasibility of implementation. NMFS
and the Navy would then analyze the
input from the Monitoring Workshop
participants and determine the best way
forward from a national perspective.
Subsequent to the Monitoring
Workshop, modifications would be
applied to monitoring plans as
appropriate.
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Integrated Comprehensive Monitoring
Program
In addition to the Monitoring Plan for
the SOCAL Range Complex, the Navy
will complete the Integrated
Comprehensive Monitoring Program
(ICMP) Plan by the end of 2009. The
ICMP will provide the overarching
coordination that will support
compilation of data from range-specific
monitoring plans (e.g., SOCAL Range
Complex plan) as well as Navy funded
research and development (R&D)
studies. The ICMP will coordinate the
monitoring program’s progress towards
meeting its goals and develop a data
management plan. The ICMP will be
evaluated annually to provide a matrix
for progress and goals for the following
year, and will make recommendations
on adaptive management for refinement
and analysis of the monitoring methods.
The primary objectives of the ICMP
are to:
• Monitor and assess the effects of
Navy activities on protected species;
• Ensure that data collected at
multiple locations is collected in a
manner that allows comparison between
and among different geographic
locations;
• Assess the efficacy and practicality
of the monitoring and mitigation
techniques;
• Add to the overall knowledge-base
of marine species and the effects of
Navy activities on marine species.
The ICMP will be used both as: (1) A
planning tool to focus Navy monitoring
priorities (pursuant to ESA/MMPA
requirements) across Navy Range
Complexes and Exercises; and (2) an
adaptive management tool, through the
consolidation and analysis of the Navy’s
monitoring and watchstander data, as
well as new information from other
Navy programs (e.g., R&D), and other
appropriate newly published
information.
In combination with the 2011
Monitoring Workshop and the adaptive
management component of the SOCAL
Range Complex rule and the other
planned Navy rules (e.g., AFAST and
HRC), the ICMP could potentially
provide a framework for restructuring
the monitoring plans and allocating
monitoring effort based on the value of
particular specific monitoring proposals
(in terms of the degree to which results
would likely contribute to stated
monitoring goals, as well as the likely
technical success of the monitoring
based on a review of past monitoring
results) that have been developed
through the ICMP framework, instead of
allocating based on maintaining an
equal (or commensurate to effects)
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distribution of monitoring effort across
Range complexes. For example, if
careful prioritization and planning
through the ICMP (which would include
a review of both past monitoring results
and current scientific developments)
were to show that a large, intense
monitoring effort in Hawaii would
likely provide extensive, robust and
much-needed data that could be used to
understand the effects of sonar
throughout different geographical areas,
it may be appropriate to have other
Range Complexes dedicate money,
resources, or staff to the specific
monitoring proposal identified as ‘‘high
priority’’ by the Navy and NMFS, in lieu
of focusing on smaller, lower priority
projects divided throughout their home
Range Complexes.
The ICMP will identify:
• A means by which NMFS and the
Navy would jointly consider the
previous year’s monitoring results and
advancing science to determine if
modifications are needed in mitigation
or monitoring measures to better effect
the goals laid out in the Mitigation and
Monitoring sections of the SOCAL
Range Complex rule.
• Guidelines for prioritizing
monitoring projects.
• If, as a result of the workshop and
similar to the example described in the
paragraph above, the Navy and NMFS
decide it is appropriate to restructure
the monitoring plans for multiple ranges
such that they are no longer evenly
allocated (by Range Complex), but
rather focused on priority monitoring
projects that are not necessarily tied to
the geographic area addressed in the
rule, the ICMP will be modified to
include a very clear and unclassified
record-keeping system that will allow
NMFS and the public to see how each
Range Complex/project is contributing
to all of the ongoing monitoring
(resources, effort, money, etc.).
Past Monitoring in the SOCAL Range
Complex
The proposed rule contained a
detailed review of the previous marine
mammal monitoring conducted in the
SOCAL Range Complex, which was
conducted in compliance with the terms
and conditions of multiple biological
opinions issued for MFAS activities (73
FR 60836, pages 60873–60875). No
changes have been made to the
discussion contained in the proposed
rule.
Adaptive Management
The final regulations governing the
take of marine mammals incidental to
Navy activities in the SOCAL Range
Complex will contain an adaptive
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management component. Our
understanding of the effects of MFAS/
HFAS and explosives on marine
mammals is still in its relative infancy,
and yet the science in this field
continues to improve. These
circumstances make the inclusion of an
adaptive management component both
valuable and necessary within the
context of 5-year regulations for
activities that have been associated with
marine mammal mortality in certain
circumstances and locations (though not
the SOCAL Range Complex). The use of
adaptive management will give NMFS
the ability to consider new data from
different sources to determine (in
coordination with the Navy) on an
annual basis if mitigation or monitoring
measures should be modified or added
(or deleted) if new data suggests that
such modifications are appropriate (or
are not appropriate) for subsequent
annual LOAs.
Following are some of the possible
sources of applicable data:
• Results from the Navy’s monitoring
from the previous year (either from the
SOCAL Range Complex or other
locations).
• Findings of the Workshop that the
Navy will convene in 2011 to analyze
monitoring results to date, review
current science, and recommend
modifications, as appropriate to the
monitoring protocols to increase
monitoring effectiveness.
• Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP, which
is discussed elsewhere in this
document).
• Results from specific stranding
investigations (either from the SOCAL
Range Complex or other locations,
involving the coincident MFAS/HFAS
of explosives training or not involving
the coincident use).
• Results from the Long Term
Prospective Study described below.
• Results from general marine
mammal and sound research (funded by
the Navy (described below) or
otherwise).
Mitigation measures could be
modified or added (or deleted) if new
data suggests that such modifications
would have (or do not have) a
reasonable likelihood of accomplishing
the goals of mitigation laid out in this
final rule and if the measures are
practicable. NMFS would also
coordinate with the Navy to modify or
add to (or delete) the existing
monitoring requirements if the new data
suggest that the addition of (or deletion
of) a particular measure would more
effectively accomplish the goals of
monitoring laid out in this final rule.
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The reporting requirements associated
with this rule are designed to provide
NMFS with monitoring data from the
previous year to allow NMFS to
consider the data and issue annual
LOAs. NMFS and the Navy will meet
annually (prior to LOA issuance, except
in the year of the Monitoring Workshop)
to discuss the monitoring reports, Navy
R&D developments, and current science
and whether mitigation or monitoring
modifications are appropriate.
Reporting
In order to issue an ITA for an
activity, Section 101(a)(5)(A) of the
MMPA states that NMFS must set forth
‘‘requirements pertaining to the
monitoring and reporting of such
taking’’. Effective reporting is critical to
ensure compliance with the terms and
conditions of an LOA, and to provide
NMFS and the Navy with data of the
highest quality based on the required
monitoring.
As NMFS noted in its proposed rule,
additional detail has been added to the
reporting requirements since they were
outlined in the proposed rule. The
updated reporting requirements are all
included below. A subset of the
information provided in the monitoring
reports may be classified and not
releasable to the public.
NMFS will work with the Navy to
develop tables that allow for efficient
submission of the information required
below.
General Notification of Injured or Dead
Marine Mammals
Navy personnel will ensure that
NMFS (regional stranding coordinator)
is notified immediately (or as soon as
operational security allows) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater
explosive detonations. The Navy will
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) (including
carcass condition if the animal is dead),
location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). The Stranding
Response Plan contains more specific
reporting requirements for specific
circumstances.
Annual SOCAL Range Complex
Monitoring Plan Report
The Navy shall submit a report
annually on October 1 describing the
implementation and results (through
August 1 of the same year) of the
SOCAL Range Complex Monitoring
Plan, described above. Data collection
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methods will be standardized across
range complexes to allow for
comparison in different geographic
locations. Although additional
information will also be gathered,
marine mammal observers (MMOs)
collecting marine mammal data
pursuant to the SOCAL Range Complex
Monitoring Plan shall, at a minimum,
provide the same marine mammal
observation data required in the MFAS/
HFAS major Training Exercises section
of the Annual SOCAL Range Complex
Exercise Report referenced below.
The SOCAL Range Complex
Monitoring Plan Report may be
provided to NMFS within a larger report
that includes the required Monitoring
Plan Reports from multiple Range
Complexes.
Annual SOCAL Range Complex Exercise
Report
The Navy will submit an Annual
SOCAL Range Complex Exercise Report
on October 1 of every year (covering
data gathered through August 1). This
report shall contain the subsections and
information indicated below.
MFAS/HFAS Major Training Exercises
This section shall contain the
following information for Integrated,
Coordinated, and Major Training
Exercises (MTEs), which include Ship
ASW Readiness and Evaluation
Measuring (SHAREM), Sustainment
Exercises, Integrated ASW Course Phase
II (IAC2), Composite Training Unit
Exercises (COMPTUEX), and Joint Task
Force Exercises (JTFEX) conducted in
the SOCAL Range Complex:
(a) Exercise Information (for each
MTE):
(i) Exercise designator.
(ii) Date that exercise began and ended.
(iii) Location.
(iv) Number and types of active sources
used in the exercise.
(v) Number and types of passive
acoustic sources used in exercise.
(vi) Number and types of vessels,
aircraft, etc., participating in
exercise.
(vii) Total hours of observation by
watchstanders.
(viii) Total hours of all active sonar
source operation.
(ix) Total hours of each active sonar
source (along with explanation of
how hours are calculated for
sources typically quantified in
alternate way (buoys, torpedoes,
etc.)).
(x) Wave height (high, low, and average
during exercise).
(b) Individual marine mammal
sighting info (for each sighting in each
MTE):
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(i) Location of sighting.
(ii) Species (if not possible—indication
of whale/dolphin/pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial Detection Sensor.
(vi) Indication of specific type of
platform observation made from
(including, for example, what type
of surface vessel, i.e., FFG, DDG, or
CG).
(vii) Length of time observers
maintained visual contact with
marine mammal(s).
(viii) Wave height (in feet).
(ix) Visibility.
(x) Sonar source in use (y/n).
(xi) Indication of whether animal is
<200yd, 200–500yd, 500–1000yd,
1000–2000yd, or >2000yd from
sonar source in (x) above.
(xiii) Mitigation Implementation—
Whether operation of sonar sensor
was delayed, or sonar was powered
or shut down, and how long the
delay was.
(xiv) If source in use (x) is hullmounted,
true bearing of animal from ship,
true direction of ship’s travel, and
estimation of animal’s motion
relative to ship (opening, closing,
parallel).
(xv) Observed behavior—Watchstanders
shall report, in plain language and
without trying to categorize in any
way, the observed behavior of the
animals (such as animal closing to
bow ride, paralleling course/speed,
floating on surface and not
swimming, etc.).
(c) An evaluation (based on data
gathered during all of the MTEs) of the
effectiveness of mitigation measures
designed to avoid exposing animals to
mid-frequency sonar. This evaluation
shall identify the specific observations
that support any conclusions the Navy
reaches about the effectiveness of the
mitigation.
ASW Summary
This section shall include the
following information as summarized
from both MTEs and non-major training
exercises (unit-level exercises, such as
TRACKEXs):
(i) Total annual hours of each type of
sonar source (along with explanation of
how hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.)).
(iv) Cumulative Impact Report—To
the extent practicable, the Navy, in
coordination with NMFS, shall develop
and implement a method of annually
reporting non-major (i.e., other than
MTEs) training exercises utilizing hullmounted sonar. The report shall present
an annual (and seasonal, where
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practicable) depiction of non-major
training exercises geographically across
the SOCAL Range Complex. The Navy
shall include (in the SOCAL Range
Complex annual report) a brief annual
progress update on the status of the
development of an effective and
unclassified method to report this
information until an agreed-upon (with
NMFS) method has been developed and
implemented.
SINKEXs
This section shall include the
following information for each SINKEX
completed that year:
(a) Exercise info:
(i) Location.
(ii) Date and time exercise began and
ended.
(iii) Total hours of observation by
watchstanders before, during, and
after exercise.
(iv) Total number and types of rounds
expended/explosives detonated.
(v) Number and types of passive
acoustic sources used in exercise.
(vi) Total hours of passive acoustic
search time.
(vii) Number and types of vessels,
aircraft, etc., participating in
exercise.
(viii) Wave height in feet (high, low and
average during exercise).
(ix) Narrative description of sensors and
platforms utilized for marine
mammal detection and timeline
illustrating how marine mammal
detection was conducted.
(b) Individual marine mammal
observation (by Navy lookouts) info:
(i) Location of sighting.
(ii) Species (if not possible—indication
of whale/dolphin/pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial detection sensor.
(vi) Length of time observers maintained
visual contact with marine
mammal.
(vii) Wave height.
(viii) Visibility.
(ix) Whether sighting was before,
during, or after detonations/
exercise, and how many minutes
before or after.
(x) Distance of marine mammal from
actual detonations (or target spot if
not yet detonated)—use four
categories to define distance: (1)
The modeled injury threshold
radius for the largest explosive used
in that exercise type in that
OPAREA (738 m for SINKEX in the
SOCAL Range Complex); (2) the
required exclusion zone (1 nm for
SINKEX in SOCAL Range
Complex); (3) the required
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3891
observation distance (if different
than the exclusion zone (2 nm for
SINKEX in SOCAL Range
Complex); and (4) greater than the
required observed distance. For
example, in this case, the observer
would indicate if < 738 m, from 738
m–1 nm, from 1 nm–2 nm, and > 2
nm.
(xi) Observed behavior—Watchstanders
will report, in plain language and
without trying to categorize in any
way, the observed behavior of the
animals (such as animal closing to
bow ride, paralleling course/speed,
floating on surface and not
swimming etc.), including speed
and direction.
(xii) Resulting mitigation
implementation—Indicate whether
explosive detonations were
delayed, ceased, modified, or not
modified due to marine mammal
presence and for how long.
(xiii) If observation occurs while
explosives are detonating in the
water, indicate munition type in
use at time of marine mammal
detection.
Improved Extended Echo-Ranging
System (IEER) and Advanced Extended
Echo-Ranging System (AEER) Summary
This section shall include an annual
summary of the following IEER/AEER
information:
(i) Total number of IEER and AEER
events conducted in the SOCAL
Range Complex.
(ii) Total expended/detonated rounds
(buoys).
(iii) Total number of self-scuttled IEER
rounds.
Explosives Summary
The Navy is in the process of
improving the methods used to track
explosive use to provide increased
granularity. To the extent practicable,
the Navy will provide the information
described below for all of their
explosive exercises. Until the Navy is
able to report in full the information
below, they will provide an annual
update on the Navy’s explosive tracking
methods, including improvements from
the previous year.
(i) Total annual number of each type of
explosive exercise (of those
identified as part of the ‘‘specified
activity’’ in this final rule)
conducted in the SOCAL Range
Complex.
(ii) Total annual expended/detonated
rounds (missiles, bombs, etc.) for
each explosive type.
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Sonar Exercise Notification
The Navy shall submit to the NMFS
Office of Protected Resources (specific
contact information to be provided in
LOA) either an electronic (preferably) or
verbal report within fifteen calendar
days after the completion of any MTE
(Sustainment, IAC2, SHAREM,
COMPTUEX, or JTFEX) indicating:
(1) Location of the exercise.
(2) Beginning and end dates of the
exercise.
(3) Type of exercise.
SOCAL Range Complex 5-Yr
Comprehensive Report
The Navy shall submit to NMFS a
draft report that analyzes and
summarizes all of the multi-year marine
mammal information gathered during
ASW and explosive exercises for which
annual reports are required (Annual
SOCAL Range Complex Exercise
Reports and SOCAL Range Complex
Monitoring Plan Reports). This report
will be submitted at the end of the
fourth year of the rule (November 2012),
covering activities that have occurred
through June 1, 2012.
Comprehensive National ASW Report
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By June, 2014, the Navy shall submit
a draft National Report that analyzes,
compares, and summarizes the active
sonar data gathered (through January 1,
2014) from the watchstanders and
pursuant to the implementation of the
Monitoring Plans for the SOCAL Range
Complex, the Atlantic Fleet Active
Sonar Training, the HRC, the Marianas
Range Complex, the Northwest Training
Range, the Gulf of Alaska, and the East
Coast Undersea Warfare Training Range.
The Navy shall respond to NMFS
comments and requests for additional
information or clarification on the
SOCAL Range Complex Comprehensive
Report, the Comprehensive National
ASW report, the Annual SOCAL Range
Complex Exercise Report, or the Annual
SOCAL Range Complex Monitoring Plan
Report (or the multi-Range Complex
Annual Monitoring Plan Report, if that
is how the Navy chooses to submit the
information) if submitted within 3
months of receipt. These reports will be
considered final after the Navy has
addressed NMFS’ comments or
provided the requested information, or
three months after the submittal of the
draft if NMFS does not comment by
then.
SOCAL
Comments and Responses
On October 14, 2008 (73 FR 60836),
NMFS published a proposed rule in
response to the Navy’s request to take
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marine mammals incidental to military
readiness training exercises in SOCAL
and requested comments, information
and suggestions concerning the request.
During the 30-day public comment
period, NMFS received 8 comments
from private citizens, comments from
the Marine Mammal Commission
(MMC) and several sets of comments
from non-governmental organizations,
including, the Natural Resources
Defense Council (NRDC) (which
commented on behalf of The Humane
Society of the United States, the
International Fund for Animal Welfare,
Whale and Dolphin Conservation
Society, Cetacean Society International,
Pamlico Tar River Foundation, League
for Coastal Protection, and Ocean
Futures Society and its founder JeanMichel Cousteau), the Cascadia
Research Collective (CRC), Ziphius
EcoServices, and Smultea
Environmental Sciences, LLC. The
comments are summarized and sorted
into general topic areas and are
addressed below. Full copies of the
comment letters may be accessed at
www.regulations.gov.
Monitoring and Reporting
Comment 1: One commenter stated
that ‘‘It is advisable to hold a multi-day
workshop to discuss controversial
issues related to the problem.’’ The
commenter further indicated that the
workshop should include
representatives from the Navy, NMFS,
relevant marine mammal researchers,
NGOs (e.g., NRDC), and invited experts
on certain topics of interest. The goal of
the workshop should be to move
towards consensus on a way forward for
the monitoring plan. Another
commenter suggested that outside
expert review of the ICMP by
professional marine mammal biologists
was needed.
Response: NMFS believes that a
workshop consisting of the Navy,
NMFS, researchers, invited experts, and
other interested parties, in combination
with an adaptive management plan that
allows for modification to the
monitoring plan, would provide a
means for the Navy to potentially make
changes to the Monitoring Plan that
would more effectively accomplish
some of the goals of monitoring set forth
earlier in the Monitoring section. NMFS
and the Navy have coordinated on this
point and the Navy will convene a
workshop, to include (among others)
outside marine mammal experts, in
2011. The workshop and how it will
interact with the adaptive management
component are discussed in the
Monitoring Workshop section of this
final rule. The Monitoring Workshop
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participants will be asked to submit
individual recommendations to the
Navy and NMFS, and both agencies will
work together to determine whether
modifications to the SOCAL Range
Complex monitoring are necessary
based on the recommendations. As
necessary, NMFS would incorporate any
changes into future LOAs and future
rules. However, NMFS disagrees with
the commenter’s suggestion that the
workshop participants seek to achieve
consensus on a way forward for the
monitoring plan. NMFS has statutory
responsibility to prescribe regulations
pertaining to monitoring and reporting,
and will in coordination with the Navy,
develop the most effective and
appropriate monitoring and reporting
protocols for future authorizations.
Comment 2: Two commenters made
several recommendations regarding the
formatting and understandability of the
monitoring plan, including
recommending additional text. For
example, one commenter recommended
the Navy add a list of acronyms and
another recommended adding text
explaining that dropping sonobuoys
from monitoring observation aircraft is
another potential method of PAM whose
feasibility and utility should be assessed
as part of the SCMP.
Response: NMFS and the Navy
incorporated these recommendations
where appropriate. For example, both of
the above examples were incorporated.
However, we did not incorporate the
commenter’s recommendations in all
cases, if we believed doing so, for
example, would needlessly lengthen
and complicate the Plan or generally be
duplicative with the analytical contents
of the rule.
Comment 3: One commenter stated:
‘‘The Navy improperly assumes that
they have no impact on the marine
mammals. It is clear that the draft plan
begins with the assumption that the
Navy has no impact on marine
mammals, or that the current mitigation
is adequate to eliminate impacts. This is
not supported by facts, and it
invalidates the entire purpose of the
plan. The Navy must acknowledge that
sonar testing may indeed impact marine
mammals and provide references, and
must be willing to work as an active
partner in a plan to investigate the
extent and severity of such impacts, and
how to reduce them to insignificant
levels. Otherwise, this entire exercise is
just ‘window dressing’ and will be a
major waste of taxpayer dollars.’’
Response: NMFS disagrees with this
commenter’s assertion. It is possible that
the commenter mistook the fact that the
Navy phrased some of their goals as null
hypotheses (‘‘If marine mammals and
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sea turtles are exposed to MFAS, what
are their behavioral responses? Are they
different at various levels?’’) to mean
that they think there are no effects. The
Navy’s LOA application and EIS clearly
discuss the potential adverse effects that
marine mammals may experience when
exposed to MFAS/HFAS and explosive
detonations. The Navy has and will
continue to work as an active partner to
investigate the extent and severity of the
impacts and how to reduce them (see
Navy Research section of this final rule).
Regarding the issue of the mitigation
being adequate to eliminate impacts,
nowhere does either the Navy or NMFS
indicate that the current mitigation will
eliminate impacts. The MMPA requires
that NMFS put forth the means of
effecting the least practicable adverse
impacts. As discussed in the Mitigation
section of the proposed rule, NMFS has
determined that the final required
mitigation accomplishes this. If it were
possible to eliminate impacts to marine
mammals, an MMPA authorization
would not be necessary.
Comment 4: Two commenters were
concerned that the Navy used the term
‘‘relative distance’’ when describing the
data that would be gathered for marine
mammals and sound sources and
indicated that precise measurements are
needed to draw accurate conclusions.
Response: GPS measurements are
used for the majority of Navy data, both
for ship tracks and marine mammal
sightings. The word ‘‘relative’’ was used
because in some cases the Navy cannot
report exactly where their exercise is for
security reasons, but they can report
exactly where the marine mammal was
relative to the sound source.
Comment 5: A few commenters asked
why the Navy did not consider
additional survey methods, or
modifications to the existing methods,
beyond those currently included in the
plan, such as: dropping sonobuoys from
airplanes, specified focal follows of one
animal before, during, and after sonar;
photo-identification of marine mammals
to look at residency patterns; or doing
biopsy sampling to assess stress
hormones.
Response: There are many different
methods available with which to
monitor marine mammals and the Navy
considered a wide range of methods in
the development of their plan. NMFS
considered all of the public comments
(including the recommended additional
survey methods) received during this
rulemaking. Some of the methods
suggested by the public, such as the
photo-identification method, would
likely be feasible and provide useful
information (and in fact, the Navy will
take photographs whenever feasible),
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while other methods, such as biopsy
sampling (which would require a new
research permit), would be more
difficult both financially and
operationally. Nevertheless, the Navy
must work within the framework of the
available resources and the operational
constraints associated with doing work
in the vicinity of a complex military
exercise. NMFS provided input during
the development of the plan and
believes that results from the required
monitoring will provide valuable
information regarding the effects of
MFAS on marine mammals.
Additionally, by including the
Monitoring Plan as a requirement of the
regulations and LOA, NMFS is
compliant with the MMPA requirement
to prescribe regulations setting forth the
requirements pertaining to the
monitoring and reporting of taking. That
being said, the Navy and NMFS
understand the importance of marine
mammal monitoring to determine the
effects of MFAS, which is why the Navy
agreed to conduct the Workshop
referred to in Comment #1 during which
the workshop participants will review
and assess the monitoring results (from
this Monitoring Plan and others from
other Range complexes and areas) and
make informed recommendations for
how to move forward with the best
monitoring strategy.
Comment 6: One commenter asked
that the Navy specify somewhere in the
Monitoring Plan that any potentially
stranded animals will be photographed
for individual identification purposes.
Response: When possible, every
attempt will be made to
opportunistically collect concurrent
digital video and digital photographs of
animals under observation by both
vessels and aircraft. Direct experience
with aerial monitoring within the
Hawaii and SOCAL Range Complexes in
2008 revealed the value of these
techniques for on-site and off-site
species identification or confirmation,
and for assistance in reviewing a given
animal’s behavioral state after the
survey. Language to this effect has been
added to the Monitoring Plan.
Comment 7: One commenter
questioned who will conduct the
Adaptive Management Review and
whether professional marine mammal
and sea turtle biologists will be involved
as advisors on a regular basis.
Response: The NMFS and the Navy
will conduct the Adaptive Management
Reassessment review to examine the
prior year’s monitoring lessons learned,
integrate new science, and re-direct
monitoring based on input from the
scientific community. As mentioned in
comment 1, professional marine
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mammal biologists will be involved in
the 2011 Monitoring Workshop.
Comment 8: One commenter noted
that there is a lot of emphasis on
collection of data by Navy
watchstanders, but the Navy must
acknowledge the limitation of these
kinds of data. The relatively low level
of training and experience by these
people (in relation to professional
marine mammal biologists) will make
the data collected of little value.
Another commenter similarly notes that
the marine species awareness training
consists primarily of watching a DVD,
which is insufficient to ensure that they
accurately detect many species.
Response: The vast majority of the
monitoring (pursuant to the monitoring
plan) will be conducted by independent
marine mammal scientists. Alternately,
Navy lookouts are responsible for
detecting marine mammal presence
within the safety zone so that the
mitigation can be implemented. Navy
lookouts are specifically trained to
detect anomalies in the water around
the ship and both the safety of Navy
personnel and success in the training
exercise depend on the lookout being
able to detect objects (or marine
mammals) effectively around the ship.
NMFS has reviewed the Navy’s After
Action Reports from previous exercises
and they show that lookouts are
detecting marine mammals, and
implementing sonar shutdowns as
required when they do. That said, the
SOCAL Range Complex Monitoring Plan
contains a study in which Navy
lookouts will be on watch
simultaneously with non-Navy marine
mammal observers and their detection
rates will be compared. Though Navy
lookouts are not trained biologists and
may not always be able to identify a
marine mammal to species, NMFS
believes that if data is gathered
systematically and in sufficient detail
(as described in the Reporting section of
the rule), Navy lookouts will provide
important encounter rate data that will
allow comparisons between lookouts
and MMOs, as well as between when
sonar is on or off.
Comment 9: One commenter stated
that it would seem to be a conflict of
interest to be using Navy personnel to
monitor training activity areas for
marine mammals [during their own
activities].
Response: The Navy is responsible for
both the funding and implementation of
a substantial amount of marine mammal
and acoustic research and NMFS has no
concerns regarding the objectivity of the
reported results from either these
research projects or the monitoring
required pursuant to the MMPA
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authorization. It is definitely not a
conflict of interest since the statute
requires a permit holder to comply with
regulations related to the incidental
taking of marine mammals, including
monitoring and reporting requirements.
Comment 10: During aerial surveys,
information on headings/orientation of
animals should be collected as these
data can later be examined to assess
movement/response of animals relative
to locations and received sound levels
of MFAS and underwater detonations.
Response: As NMFS noted in the
proposed rule, additional detail has
been added to the Reporting
Requirements section of the final rule. A
requirement that Navy lookouts report
the relative directions of both the
marine mammals and the sonar source
has been included. NMFS also included
a requirement that the MMOs collecting
data for the Monitoring Plan collect, at
a minimum, the same data outlined in
the Reporting Requirements section for
the Navy lookouts.
Comment 11: Commenters questioned
whether the Navy had considered
whether a statistically sound sample
size had been developed to answer the
questions that monitoring is trying to
answer.
Response: The Navy will contract a
team of marine mammal experts to
implement the monitoring plan and
fine-tune the sample size and analysis
parameters. The data from the SOCAL
Range Complex will be pooled (as
appropriate) with data collected from
other range complexes to maximize data
collection each year. No conclusions
will be made without a statistically
valid sample size.
Comment 12: One commenter stated:
‘‘The Navy should establish a long-term
research program, perhaps conducted by
NMFS or by an independent agent, on
the distribution, abundance, and
population structuring of protected
species on the SOCAL Range Complex,
with the goal of supporting adaptive
geographic avoidance of high-value
habitat.’’ Another commenter suggests
that the Navy should conduct research
and development of technologies to
reduce the impacts of active acoustic
sources on marine mammals.
Response: The MMPA does not
require that individuals who have
received an incidental take
authorization conduct research. As
mentioned above, the mitigation EA
addresses geographic avoidance of highvalue habitat. Separately, the Navy has
voluntarily developed and funded a
number of research plans that are
designed to address technologies to
reduce the impacts of active acoustic
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sources on marine mammals (see
Research section).
Mitigation
Comment 13: The Marine Mammal
Commission recommends that NMFS:
(a) Clarify which monitoring and
mitigation measures will be required, in
light of the fact that a revised
Monitoring Plan was posted after the
proposed rule was published.
(b) Require performance testing and
validation of those measures (and the
MMC suggests that NMFS did not
review, and the rule does not include
reference to, five post-exercise reports
that the Navy submitted to us for 2006/
2007 exercises in the SOCAL Range
Complex).
(c) Require new measures to address
remaining monitoring and mitigation
shortcomings. The MMC suggests that
visual and passive acoustic monitoring
offer only limited detection capability
but notes that NMFS asserts that more
than 60 potential lethal or injurious
takes have been mitigated to zero by
posting visual observers and
opportunistic monitoring using
sonobuoys and other existing passive
acoustic sensing capabilities.
(d) Work with the Navy to develop a
database for storing original records of
marine mammal interactions; the
database should meet the Navy’s
security requirements but also maintain
what are potentially valuable records
about the Navy’s interactions with and
effects on marine mammals. The MMC
notes that the proposed rule indicates
that the ship’s logs of sightings, powerdowns, and other mitigation actions are
retained only for 30 days.
Response: Following are responses to
MMC’s alphabetized sub-comments:
(a) The final required mitigation
measures are exactly the same as those
described in the proposed rule. As
described in the proposed rule, the
Monitoring Plan contains a table that
generally describes the level of effort
that the Navy has committed to in the
monitoring, but the Navy continued to
develop and improve the Monitoring
Plan for the SOCAL Range Complex
(based on public comments, among
other input) throughout the MMPA and
ESA processes. The Monitoring Plan
will be finalized prior to the issuance of
the first LOA, but we note that
flexibility remains for the
implementation team (the independent
scientist contractors that the Navy will
hire to conduct the monitoring) to
further refine the specific protocols as
appropriate.
(b) Navy lookouts are specifically
trained to detect anomalies in the water
around the ship and both the safety of
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Navy personnel and success in the
training exercise depend on the lookout
being able to detect objects (or marine
mammals) effectively around the ship.
NMFS has reviewed the Navy’s After
Action Reports from previous exercises
and they show that lookouts are
detecting marine mammals and
implementing sonar shutdowns as
required. That said, the SOCAL Range
Complex Monitoring Plan contains a
study in which Navy lookouts will be
on watch simultaneously with nonNavy marine mammal observers and
their detection rates will be compared.
Additionally, the regulations and
subsequent authorization would require
the Navy to provide ‘‘an evaluation
(based on data gathered during all of the
major training exercises) of the
effectiveness of mitigation measures
designed to avoid exposing marine
mammals to mid-frequency sonar. This
evaluation shall identify the specific
observations that support any
conclusions the Navy reaches about the
effectiveness of the mitigation included
in the authorization.’’ Last, the rule
contains an adaptive management
component that specifies that NMFS
and the Navy will meet on an annual
basis to evaluate the Navy Reports (on
both Navy lookout observations as well
as Monitoring Plan reporting) and other
new information (such as Navy R&D
developments or new science) to
ascertain whether mitigation or
monitoring modifications are
appropriate.
Contrary to the MMC’s assertion,
NMFS included both a summary table of
(Table 7 in proposed rule), and general
conclusions related to, 12 post exercise
reports that the Navy submitted for
exercises conducted in 2006 and 2007.
NMFS agrees that the review of postexercise reports is critical, and through
the implementation of the more rigorous
reporting requirements that have been
laid out in the final rule (versus the
proposed rule) we should be able to
reach well-supported conclusions
regarding the effects of MFAS on marine
mammals.
(c) As described in the proposed rule,
NMFS’s analysis does not assert that
60+ injuries or mortalities are
completely alleviated by mitigation
implementation. Rather, we explain
that, in the first place, the model that
estimated 60 injuries and mortalities
does not take into consideration at all
that a subset of animals will avoid
operating sound sources (or even vessels
without operating sources), which
means that fewer than 60 animals would
be likely to get close enough to be
exposed to levels expected to result in
injury or death. For MFAS, animals
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would need to approach within 10 m of
the sound source to be exposed to levels
likely to result in injury. For explosives,
the larger charges have effects at greater
distances, but they also have very
rigorous clearance procedures that
include monitoring the area for 2 hours
in advance of the exercise. Nonetheless,
NMFS acknowledges the opportunity
for improvement via the use of
dedicated passive or active sonar to
detect marine mammals for mitigation
implementation. However, current
technology does not allow the Navy to
detect, identify, and localize marine
mammals and transmit this information
to operators real-time while also not
substantially reducing the effectiveness
of the fast-paced and complicated
exercises that the Navy must conduct.
The Navy is committed, however, to
technological development in the area
of marine mammal protection and is
currently funding multiple research
projects towards this goal (see Research
section).
(d) Though the original ship logs are
destroyed after 30 days, the information
pertaining to marine mammal
observations and mitigation
implementation is passed along to
environmental compliance staff who are
responsible for producing reports for
NMFS and who already have a system
for retaining the needed information.
However, under the ICMP, NMFS will
work with the Navy to ensure that all of
the needed information is saved (in a
standard form across geographic areas),
which could potentially include the
development of a new database.
Comment 14: One commenter noted
that the training exercises that the Navy
proposes to conduct in the Southern
California range from 2009 to 2014 are
apparently very similar to those that
have in the past provoked extended
litigation against the Navy by
environmental groups (e.g., the RIMPAC
litigation in 2006 and the ongoing
SOCAL case, NRDC v. Winters,
currently under review by the Supreme
Court). The environmental groups have,
thus far, been successful in both of their
lawsuits against the Navy and the
NMFS; each suit has required the Navy
to take much more rigorous measures to
mitigate the environmental impact of its
sonar exercises. And yet neither the
Navy nor the NMFS appears to have
incorporated the lessons of these legal
actions into their practices, as shown by
the proposed regulation released for
comment. Specifically, the NRDC
asserts that NMFS’s proposed rule, as
well as the Navy’s SOCAL Range
Complex Draft Environmental Impact
Statement (‘‘DEIS’’) (73 FR 18522 (Apr.
4, 2008)) ignores mitigation measures
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imposed specifically for the SOCAL
Range Complex by courts in California.
See NRDC v. Winter 527 F.Supp.2d
1216 (C.D. Cal. 2008), aff’d 518 F.3d 658
(9th Cir. 2008).
Response: The outcome of any
litigation is based very specifically on
the content of the administrative record
for the particular decision that is being
litigated. NMFS has worked closely
with the Navy, both in the development
of the SOCAL Range Complex EIS and
in the ESA and MMPA consultations, to
build a strong administrative record
(both procedure and content-wise) that
supports our decisions under the
applicable statutes. Both NMFS and the
Navy have incorporated lessons from
the aforementioned legal actions into
our practices. For example, the Navy
(with NMFS support as a cooperating
agency) chose to develop EISs for their
major MFAS training activities instead
of relying on an Environmental
Assessment as they did in RIMPAC
2006. However, NMFS and the Navy are
still bound to make certain findings
under different statutes, and just
because additional measures were
imposed by the court in previous
similar cases does not mean that those
measures are appropriate in the specific
context of the statutes that NMFS or the
Navy are endeavoring to comply with in
a specific case. More specifically,
though, both NMFS and the Navy have
considered the types of measures
recommended by the courts (see
Mitigation EA). Finally, the Supreme
Court (Winter v. NRDC) recently sided
with the Navy in NRDC’s challenge to
the use of mid-frequency active sonar in
the SOCAL Range Complex. The court
determined the Navy’s need to conduct
realistic training with active sonar to
respond to the threat posed by enemy
submarines plainly outweighs the
interests advanced by the plaintiffs.
Comment 15: One commenter asserts
that NMFS’s analysis ignores or
improperly discounts an array of
options that have been considered and
imposed by other active sonar users,
including avoidance of coastal waters,
high-value habitat, and complex
topography; the employment of a safety
zone more protective than the 1000-yard
power-down and 200-yard shutdown
accepted by NMFS; general passive
acoustic monitoring for whales; special
rules for surface ducting and lowvisibility conditions; monitoring and
shutdown procedures for sea turtles and
large schools of fish; and many others.
The commenter further provides a
detailed list of 30 additional measures
that should be considered. Other
commenters made additional
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3895
recommendations of mitigation
measures that should be considered.
Response: NMFS considered a wide
range of mitigation options in our
analysis, including those listed by the
commenters. In order to issue an
incidental take authorization (ITA)
under Section 101(a)(5)(A) of the
MMPA, NMFS must set forth the
‘‘permissible methods of taking
pursuant to such activity, and other
means of affecting the least practicable
adverse impact on such species or stock
and its habitat, paying particular
attention to rookeries, mating grounds,
and areas of similar significance.’’ The
National Defense Authorization Act
(NDAA) of 2004 amended the MMPA as
it relates to military-readiness activities
(which these Navy activities are) and
the incidental take authorization
process such that ‘‘least practicable
adverse impact’’ shall include
consideration of personnel safety,
practicality of implementation, and
impact on the effectiveness of the
‘‘military readiness activity’’. NMFS
worked with the Navy to identify
practicable and effective mitigation
measures, which included a careful
balancing of the likely benefit of any
particular measure to the marine
mammals with the likely effect of that
measure on personnel safety,
practicality of implementation, and
impact on the ‘‘military-readiness
activity’’. NMFS developed an
Environmental Assessment (EA) that
analyzes a suite of possible mitigation
measures in regard to potential benefits
for marine mammals (see goals of
mitigation in the Mitigation section of
this proposed rule) and practicability for
the Navy. That EA, which considered all
of the measures recommended by these
public comments, is currently available
on the NMFS Web site (https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications) and has
been relied upon to inform NMFS’s
MMPA decision.
Comment 16: One commenter
suggests that the graded response steps
for MFAS based on the distance at
which marine mammals are sighted
does not make sense given the high
proportion of time many marine
mammal species, especially long-divers,
spend underwater. A beaked whale
sighted in the path of the vessel 600
yards ahead that then dives would only
require a decrease in source level by 6
dB, even though the trajectory of the
ship would take it directly over the
animal while it is underwater.
Response: The next ‘‘graded’’
mitigation measure says ‘‘Should the
marine mammal be detected within or
closing to inside 200 yds (183 m) of the
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sonar dome, active sonar transmissions
shall cease.’’ The ‘‘or closing’’ part of
this measure ensures that if the Navy
vessel is headed straight at an animal,
they will use the appropriate measure.
Additionally, review of the Navy’s afteraction reports shows that in the vast
majority of marine mammal detections
within 1000 yds, the Navy immediately
shuts down the sonar, without going
through the power-down step.
Comment 17: NRDC recommends
prescription of specific mitigation
requirements for individual categories
(or sub-categories) of testing and
training activities, in order to maximize
mitigation given varying sets of
operational needs. Also, the Navy
should require that other nations abide
by U.S. mitigation measures when
training in the SOCAL Range Complex,
except where their own measures are
more stringent.
Response: The Navy’s standard
protective measures include measures
that are specific to certain categories of
activities. For example, different
exclusion zones are utilized for hullmounted sonar and dipping sonar, and
different range clearance procedures are
used for SINKEXs and IEER sonobuoy
exercises. Pursuant to the Navy’s 2000
Policy for Environmental Compliance at
Sea, the commander or officer in charge
of a major exercise shall provide
participating foreign units with a
description of the measures to protect
the environment required of similar U.S.
units as early as reasonable in the
exercise planning process and shall
encourage them to comply. As a binding
international law, foreign sovereign
immune vessels may not be compelled
to adopt such mitigation measures.
Comment 18: The Marine Mammal
Commission recommends that NMFS
modify the Navy’s mitigation measures
by requiring that the Navy delay
resumption of full operational sonar use
following a power-down or shutdown
for 30 minutes if the sighted animal can
be identified to the species level and the
species is not deep diving and 60
minutes if it cannot be identified or is
known to be a member of a deep-diving
species such as sperm and beaked
whales. They further recommend that
NMFS allow resumption of full
operations before the end of the 30minute period (when the species can be
identified and is not a deep diver) or 60minute period (the species cannot be
determined or can be determined but is
a deep diver) only when the Navy has
good evidence that the marine mammal
seen outside the safety zone is the same
animal originally sighted within the
zone.
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Response: NMFS does not concur
with the MMC that we should expand
the delay (until sonar can be restarted
after a shutdown due to a marine
mammal sighting) to 60 minutes for
deep-diving species for the following
reasons:
• The ability of an animal to dive
longer than 30 minutes does not mean
that it will always do so. Therefore, the
60 minute delay would only potentially
add value in instances when animals
had remained under water for more than
30 minutes.
• Navy vessels typically move at 10–
12 knots (5–6 m/sec) when operating
active sonar and potentially much faster
when not. Fish et al. (2006) measured
speeds of 7 species of odontocetes and
found that they ranged from 1.4–7.30 m/
sec. Even if a vessel was moving at the
slower typical speed associated with
active sonar use, an animal would need
to be swimming near sustained
maximum speed for an hour in the
direction of the vessel’s course to stay
within the safety zone of the vessel.
Increasing the typical speed associated
with active sonar use would further
narrow the circumstances in which the
60-minute delay would add value.
• Additionally, the times when
marine mammals are deep-diving (i.e.,
the times when they are under the water
for longer periods of time) are the same
times that a large portion of their motion
is in the vertical direction, which means
that they are far less likely to keep pace
with a horizontally moving vessel.
• Given that, the animal would need
to have stayed in the immediate vicinity
of the sound source for an hour and
considering the maximum area that both
the vessel and the animal could cover in
an hour, it is improbable that this would
randomly occur. Moreover, considering
that many animals have been shown to
avoid both acoustic sources and ships
without acoustic sources, it is
improbable that a deep-diving cetacean
(as opposed to a dolphin that might bow
ride) would choose to remain in the
immediate vicinity of the source. NMFS
believes that it is unlikely that a single
cetacean would remain in the safety
zone of a Navy sound source for more
than 30 minutes.
• Last, in many cases, the lookouts
are not able to differentiate species to
the degree that would be necessary to
implement this measure. Plus, Navy
operators have indicated that increasing
the number of mitigation decisions that
need to be made based on biological
information is more difficult for the
lookouts (because it is not their area of
expertise).
NMFS does not believe that 60minute delay would add to the
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protection of marine mammals in the
vast majority of cases, while it would
definitely decrease the effectiveness of
the Navy’s training exercises by adding
further delay, and therefore we have not
required it. Regarding the MMCs second
recommendation, the current measure
says that sonar transmission will be
limited until ‘‘the animal is seen to
leave the area’’—NMFS does not believe
that further clarification is needed
regarding the fact that the Navy needs
to be sure it is the same animal.
Comment 19: One commenter states
that the Navy should engage in timely
and regular reporting to NOAA, state
coastal management authorities, and the
public to describe and verify use of
mitigation measures during testing and
training activities.
Response: The Navy will be required
to submit annual reports and these
reports will be made available to the
public upon the Notice to the public (in
the Federal Register) of the issuance of
subsequent LOAs. The reports will
include a description of the mitigation
measures implemented during major
exercises and will also include an
evaluation of the effectiveness if any
mitigation measure implemented.
Comment 20: One commenter asserts
that the Navy should avoid fish
spawning grounds and important fish
habitat. It should also avoid high-value
sea turtle habitat. The Navy should
include sea turtles in other described
mitigation measures, including safety
zones, for which floating weeds and
kelp and algal mats should be taken as
proxies for sea turtle presence.
Response: These concerns are outside
of the purview of the MMPA. Impacts to
fish spawning grounds are dealt with
pursuant to the Magnuson-Stevens Act
as it relates to Essential Fish Habitat
(EFH). NMFS Office of Habitat
Conservation found that the Navy’s
proposed action would adversely affect
EFH, but that the proposed mitigation
measures (see the Navy’s EFH
assessment in Appendix E of the
SOCAL Range Complex FEIS) would
adequately address adverse impacts to
EFH. Therefore, NMFS made no
additional EFH conservation
recommendations. Measures to reduce
impacts to sea turtles are included in
the terms and conditions of the
biological opinion that NMFS issued to
the Navy (view at: https://
www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications). Finally, it
should be noted that the Navy will be
required to alter activities if floating
weeds or kelp are seen within a
particular area (e.g., for Surface-toSurface Gunnery exercises: ‘‘Lookouts
shall visually survey for floating weeds
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and kelp. Intended impact shall not be
within 600 yds (585 m) of known or
observed floating weeds and kelp, and
algal mats’’).
Acoustic Threshold for Behavioral
Harassment
Comment 21: The NRDC submitted a
comprehensive critique of the risk
function (authored by Dr. David Bain),
which NMFS has posted on our Web
site (https://www.nmfs.noaa.gov/pr/
permits/incidental.htm#applications).
NRDC summarized some general
limitations of the risk function and
included a fairly detailed critique of the
specific structure of and parameters
chosen for use in the model. Following
are some of the general topics addressed
in the letter:
• Factors that Dr. Bain thinks should
be addressed by the model, such as
social interactions and multiple sources.
• Critique of the datasets that NMFS
used to populate the risk function
(described Level B Harasssment—Risk
Function section of the proposed rule):
(1) Controlled Laboratory Experiments
with Odontocetes (SSC Dataset); (2)
Mysticete Field Study (Nowacek et al.,
2004), and (3) Odontocete Field Data
(Haro Strait—USS Shoup).
• Consideration of some datasets that
were considered by NMFS, but not used
in the risk function.
• A critique of the parameters (A, B,
and K) used in the risk function.
• A sensitivity analysis of the
parameters (i.e., takes were modeled
while applying variable values for the
A, B, and K values).
Dr. Bain included a summary of his
concerns and an abbreviated version is
included below. Additionally (and not
included in the summary), Dr. Bain
suggested that the effect of multiple
sources may be both different and
greater than the effects of fewer sources
and provided supporting examples.
Dr. Bain’s Summary follows
(comments that were in Dr. Bain’s
summary, but have been addressed
elsewhere in this Comment Response
section are not included below):
• In summary, development of a
function that recognizes individual
variation is a step in the right direction.
• The selected equation is likely to
produce underestimates of takes due to
asymmetries in the number of
individuals affected if parameters are
either underestimated or overestimated
due to uncertainty. Thus it will be
important to use the risk function in a
precautionary manner.
• The sensitivity analysis reveals the
importance of using as many datasets as
possible. First, for historical reasons,
there has been an emphasis on high
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energy noise sources and the species
tolerant enough of noise to be observed
near them. Exclusion of the rarer
datasets demonstrating responses to low
levels of noise biases the average
parameter values, and hence
underestimates effects on sensitive
species.
• A similar mistake was made with
the right whale data. The level at which
100 percent of individuals responded
was used as the value at which 50
percent of individuals responded (B+K).
Likewise, the level at which 100 percent
of killer whales responded to midfrequency sonar is less than the value
derived for B+K in the HRC SDEIS
(Dept. Navy 2008b).
• It is likely that biological B values
should be in the range from just
detectable above ambient noise to 120
dB re 1 μPa. The resulting mathematical
B value could be tens of dB lower, not
the 120 dB re 1 μPa proposed. For many
species, risk may approach 100 percent
in the range from 120–135 dB re 1 μPa,
putting K in the 15–45 dB range.
• The A values do not seem well
supported by the data, and in any case,
are likely to be misleading in social
species as the risk function is likely to
be asymmetrical with a disproportionate
number of individuals responding at
low noise levels. Rather than one
equation fitting all species well,
parameters are likely to be species
typical.
• As realistic parameter values are
lower than those employed in the HRC
SDEIS (Dept. Navy 2008b), AFAST DEIS
(Dept. Navy 2008a) and related DEIS’s,
take numbers should be recalculated to
reflect the larger numbers of individuals
likely to be taken. The difference
between the parameter values estimated
here and those used in the SDEIS
suggests takes were underestimated by
two orders of magnitude.
Response: Many of the limitations
outlined in Dr. Bain’s document were
raised by other commenters and are
addressed elsewhere in this Comment
and Response Section and will not be
addressed again here. Below, NMFS
responds to the specific points
summarized above.
• The effects of multiple sources:
Mathematically, the Navy’s exposure
model has already accounted for takes
of animals exposed to multiple sources
in the number of estimated takes. NMFS
concurs with the commenter, however,
in noting that the severity of responses
of the small subset of animals that are
actually exposed to multiple sources
simultaneously could potentially be
greater than animals exposed to a single
source due to the fact that received
level, both SPL and SEL, would be
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slightly higher and because contextually
it could be perceived as more
threatening to an animal to receive
multiple stimuli coming from
potentially multiple directions at once
(for example, marine mammals have
been shown to respond more severely to
sources coming directly towards them,
vs. obliquely (Wartzok, 2004)).
However, it is also worth noting that
according to information provided by
the Navy, surface vessels do not
typically operate closer than 10–20
miles from another surface vessel (and
greater distance is ideal), and other
sonar sources, such as dipping sonar
and sonobuoys, are almost always used
20 or more miles away from the surface
vessel. This means that if the two most
powerful sources were operating at the
closest distance they are likely to (10
miles), in the worst case scenario,
animals that would have been exposed
to 150 dB SPL or less (taken from table
16 of the proposed rule) may be exposed
to slightly higher levels or to similar
levels or less coming from multiple
directions.
• Underestimates of takes due to
asymmetries in the number of
individuals affected when parameters
are underestimated and overestimated
due to uncertainty: The commenter’s
point is acknowledged. When a
sensitivity analysis is conducted and
parameters are varied (both higher and
lower values used)—the degree of
difference in take estimates is much
greater when the parameter is adjusted
in one direction than in the other,
which suggests the way that this
generalized model incorporates
uncertainty may not be conservative.
However, in all cases when the
adjustment of the parameter in a certain
direction results in a disproportionately
(as compared to an adjustment in the
other direction) large increase in the
number of takes, it is because the model
is now estimating that a larger
percentage of animals will be taken at
greater distances from the source. This
risk function is based completely on the
received level of sound. As discussed in
the proposed rule, there are other
contextual variables that are very
important to the way that an animal
responds to a sound, such as nearness
of the source, relative movement
(approaching or retreating), or the
animals familiarity with the source.
Southall et al. (2007) indicates that the
presence of high-frequency components
and a lack of reverberation (which are
indicative of nearness) may be more
relevant acoustic cues of spatial
relationship than simply exposure level
alone. In the SOCAL Range Complex, an
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animal exposed to between 120 and 130
dB may be more than 65 nm from the
sonar source. NMFS is not aware of any
data that describe the response of any
marine mammals to sounds at that
distance, much less data that indicate
that an animal responded in a way we
would classify as harassment at that
distance. Because of this, NMFS does
not believe it is currently possible or
appropriate to modify the model to
further address uncertainty if doing so
results in the model predicting that
much larger numbers of animals will be
taken at great distances from the source
when we have no data to suggest that
that would occur.
• Using many datasets: NMFS has
explained both in the rule, and then
again elsewhere in response to these
comments, why we chose the three
datasets we did to define the risk
function. As Dr. Bain points out, there
are datasets that report marine mammal
responses to lower levels of received
sound. However, because of the
structure of the curve NMFS is using
and what it predicts (Level B
Harassment), we need datasets that
show a response that we have
determined qualifies as harassment (in
addition to needing a source that is
adequately representative of MFAS and
reliable specific received level
information), which many of the lower
level examples do not.
• 50 percent vs. 100 percent response:
Dr. Bain asserts that two of the three
datasets (Nowacek et al., 2004 and Haro
Strait—USS SHOUP) that NMFS uses to
derive the 50 percent response
probability in the risk function actually
report a 100 percent response at the
indicated received levels. For the Haro
Strait dataset, a range of estimated
received levels at the closest approach
to the J Pod were estimated. Given that
neither the number of individual
exposures or responses were available,
the mean of this range was used as a
surrogate for the 50 percent response
probability in the development of the
risk function. For the Nowacek data,
NMFS used 139.2 dB, which is the
mean of the received levels at which 5
of 6 animals showed a significant
response to the signal. However, viewed
another way, of 6 animals, one animal
did not respond to the signal and the
other five responded at received levels
of 133 dB, 135 dB, 137 dB, 143 dB, and
148 dB, which means that 3 of the 6
animals (50 percent) showed a
significant response at 139.2 dB or less.
• 120 dB basement value: When the
broad array of data reported from
exposures across taxa and to varied
sources are reviewed, NMFS believes
that 120 dB is an appropriate B value for
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a curve designed to predict responses
that rise to the level of an MMPA
harassment (not just any response). The
available data do not support the
commenter’s assertion that risk may
approach 100 percent in the range from
120–135 dB for many species. For
example, the Southall et al. (2007)
summary of behavioral response data
clearly shows, in almost every table (for
all sound types), reports of events in
which animals showed no observable
response, or low-level responses NMFS
would not likely consider harassment,
in the 120 to 135-dB range. For the
species (the harbor porpoise) for which
the data do support that assertion,
which the Southall et al. (2007) paper
considers ‘‘particularly sensitive’’,
NMFS has implemented the use of a
species-specific step function threshold
of 120 dB SPL.
• The A value: Please see the second
bullet of this response for the first part
of the answer. NMFS concurs with the
commenter that species-specific
parameters would likely be ideal,
however there are not currently enough
applicable data to support separate
curves for each species. We note,
though, that even with species-specific
parameters, the context of the exposure
will still likely result in a substantive
variability of behavioral responses to the
same received level by the same species.
• Recalculation: For the reasons
described in the bullets above in this
response, NMFS disagrees with the
commenter’s assertion that the
parameters used in the proposed rule
and the EIS are unrealistic and that they
result in take estimates that are too
small by two orders of magnitude. We
do not believe that a recalculation is
necessary.
The science in the field of marine
mammals and underwater sound is
evolving relatively rapidly. NMFS is in
the process of revisiting our acoustic
criteria with the goal of developing a
framework (Acoustic Guidelines) that
allows for the regular and scientifically
valid incorporation of new data into our
acoustic criteria. We acknowledge that
this model has limitations, however, the
limitations are primarily based on the
lack of applicable quantitative data. We
believe that the best available science
has been used in the development of the
criteria used in this and other
concurrent Navy rules and that this
behavioral harassment threshold far
more accurately represents the number
of marine mammals that will be taken
than the criteria used in the RIMPAC
2006 authorization. We appreciate the
input from the public and intend to
consider it further as we move forward
and develop the Acoustic Guidelines.
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Comment 22: One commenter
expressed the concern that NMFS
blindly relies on TTS studies conducted
on 7 captive animals of two species (to
the exclusion of copious data on
animals in the wild) as a primary source
of data for the behavioral harassment
threshold. The commenter further
asserts that these studies (on highly
trained animals that do not represent a
normal range of variation within their
own species, as they have been housed
in a noisy bay for most of their lives)
have major deficiencies, which NMFS
ignores by using the data.
Response: The SSC Dataset
(Controlled Laboratory Experiments
with Odontocetes) is not the primary
source of data for the behavioral
harassment threshold; rather, it is one of
three datasets (the other two datasets are
from wild species exposed to noise in
the field) treated equally in the
determination of the K value (equates to
midpoint) of the behavioral risk
function. NMFS recognizes that certain
limitations may exist when one
develops and applies a risk function to
animals in the field based on captive
animal behavioral data. However, we
note that for the SSC Dataset: (1)
Researchers had superior control over
and ability to quantify noise exposure
conditions; (2) behavioral patterns of
exposed marine mammals were readily
observable and definable; and, (3)
fatiguing noise consisted of tonal noise
exposures with frequencies contained in
the tactical mid-frequency sonar
bandwidth. NMFS does not ignore the
deficiencies of these data, rather we
weighed them against the value of the
data and compared the dataset to the
other available datasets and decided
that the SSC dataset was one of the three
appropriate datasets to use in the
development of the risk function.
Comment 23: NMFS fails to include
data from the July 2004 Hanalei Bay
event, in which 150–200 melon-headed
whales were embayed for more than 24
hours during the Navy’s Rim of the
Pacific exercise. According to the
Navy’s analysis, predicted mean
received levels (from mid-frequency
sonar) inside and at the mouth of
Hanalei Bay ranged from 137.9 dB to
149.2 dB. NMFS’ failure to incorporate
these numbers into its methodology as
another data set is not justifiable.
Response: NMFS’ investigation of the
Hanalei event concluded that there was
insufficient evidence to determine
causality. There are a number of
uncertainties about sonar exposure and
other potential contributing factors and
assumptions inherent to a
reconstruction of events in which sonar
was the causative agent that simply
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preclude this determination. Because of
this, NMFS did not use the numbers
(137.9–149.2 dB) in our methodology.
Additionally, even if NMFS had
concluded that MFAS were the
causative agent, insufficient evidence
exists regarding the received level when
the animals responded (there is no
information regarding where they were
when they would have first heard the
sound).
Comment 24: One commenter stated
‘‘NMFS excludes a substantial body of
research on wild animals (and some
research on other experimental animals
as well, within a behavioral
experimental protocol). Perhaps most
glaringly, while the related DEIS
prepared for the Navy’s Atlantic Fleet
Active Sonar Training activities appears
to acknowledge the strong sensitivity of
harbor porpoises by setting an absolute
take threshold of 120 dB (SPL)—a
sensitivity that, as NMFS has noted, is
reflected in numerous wild and captive
animal studies—the agencies
improperly fail to include any of these
studies in their data set. The result is
clear bias, for even if one assumes (for
argument’s sake) that the SPAWAR data
has value, NMFS has included a
relatively insensitive species in setting
its general standard for marine
mammals while excluding a relatively
sensitive one.’’
Response: As explained in the Level
B Harassment (Risk Function) section of
the proposed rule the risk function is
based primarily on three datasets (SSC
dataset, Nowacek et al. (2004), and Haro
Strait—USS Shoup) in which marine
mammals exposed to mid-frequency
sound sources were reported to respond
in a manner that NMFS would classify
as Level B Harassment. NMFS
considered the ‘‘substantial body of
research’’ that the commenter refers to
but was unable to find other datasets
that were suitable in terms of all of the
following: The equivalency of the sound
source to MFAS, a reported behavioral
response that NMFS would definitively
consider Level B Harassment, and a
received level reported with high
confidence. The SSC dataset is only one
of three used and, in fact, the other 2
datasets (which are from wild animals—
killer whales and North Atlantic right
whales) both report behavioral
responses at substantively lower levels
(i.e., the ‘‘relatively insensitive’’ species
is not driving the values in the
function).
Separately, combined wild and
captive data support the conclusion that
harbor porpoises (high-frequency
hearing specialists) are quite sensitive to
a variety of anthropogenic sounds at
very low exposures (Southall et al.,
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2007). Southall et al. (which refer to
harbor porpoises as particularly
sensitive species) report that all
recorded exposures exceeding 140 dB
SPL induced profound and sustained
avoidance behavior in wild harbor
porpoises. Unlike for the mid-frequency
and low-frequency species, there are
also no reported instances where harbor
porpoises were exposed to higher levels
and did not have a high response score.
For these reasons, harbor porpoises are
considered especially sensitive and
NMFS determined that it is appropriate
to apply a more conservative threshold.
Comment 25: The risk function must
take into account the social ecology of
some marine mammal species. For
species that travel in tight-knit groups,
an effect on certain individuals can
adversely influence the behavior of the
whole. Should those individuals fall on
the more sensitive end of the spectrum,
the entire group or pod can suffer
significant harm at levels below what
the Navy would use as the mean. In
developing its ‘‘K’’ parameter, NMFS
must take into account the potential for
indirect effects.
Response: The risk function is
intended to define the received level of
MFAS at which exposed marine
mammals will experience behavioral
harassment. The issue the commenter
raises is related to the Navy’s exposure
model—not the risk function. However,
because of a lack of related data there
is no way to numerically address this
issue in the model. Although the point
the commenter raises could potentially
apply, one could also assert that if
certain animals in a tight knit group
were less sensitive it would have the
opposite effect on the group.
Additionally, the modeling is based on
uniform marine mammal density
(distributed evenly over the entire area
of potential effect), which does not
consider the fact that marine mammals
appearing in pods will be easier to
detect and therefore the Navy will be
more likely to implement mitigation
measures that avoid exposing the
animals to the higher levels received
within 1000m of the source.
Comment 26: One commenter asserts
that NMFS’ threshold is applied in such
a way as to preclude any assessment of
long-term behavioral impacts on marine
mammals. It does not account, to any
degree, for the problem of repetition:
The way that apparently insignificant
impacts, such as subtle changes in dive
times or vocalization patterns, can
become significant if experienced
repeatedly or over time.
Response: NMFS threshold does not
preclude any assessment of long-term
behavioral impacts on marine mammals.
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The threshold is a quantitative tool that
NMFS uses to estimate individual
behavioral harassment events.
Quantitative data relating to long-term
behavioral impacts are limited, and
therefore NMFS’ assessment of longterm behavioral impacts is qualitative in
nature (see Diel Cycle section in
Negligible Impact Analysis section).
NMFS analysis discusses the potential
significance of impacts that continue
more than 24 hours and/or are repeated
on subsequent days and, though it does
not quantify those impacts, further
indicates that these types of impacts are
not likely to occur because of the nature
of the Navy’s training activities and the
large area over which they are
conducted.
Comment 27: One commenter stated
‘‘NMFS appears to have misused data
garnered from the Haro Strait incident—
one of only three data sets it considers—
by including only those levels of sound
received by the ‘‘J’’ pod of killer whales
when the USS Shoup was at its closest
approach. These numbers represent the
maximum level at which the pod was
harassed; in fact, the whales were
reported to have broken off their
foraging and to have engaged in
significant avoidance behavior at far
greater distances from the ship, where
received levels would have been orders
of magnitude lower. We must insist that
NMFS provide the public with the
Navy’s propagation analysis for the Haro
Strait event, which it used in preparing
its 2005 Assessment of the incident.’’
Response: For the specific application
in the risk function for behavioral
harassment, NMFS used the levels of
sound received by the ‘‘J’’ pod when the
USS Shoup was at its closest approach
because a review of the videotapes and
other materials by NMFS detailing the
behavior of the animals in relation to
the location of the Navy vessels showed
that it was after the closest approach of
the vessel that the whales were observed
responding in a manner that NMFS
would classify as ‘‘harassed.’’ Though
animals were observed potentially
responding to the source at greater
distances, NMFS scientists believed that
the responses observed at greater
distances were notably less severe and
would not rise to the level of MMPA
harassment. Though the received levels
observed in relation to the lesser
responses could be used in some types
of analytical tools, the risk continuum
specifically requires that we use
received sound levels that are
representative of when MMPA
harassment likely occurred. The Navy’s
report may be viewed at: https://
www.acousticecology.org/docs/
SHOUPNavyReport0204.pdf.
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Acoustic Thresholds for TTS and PTS
Comment 28: One commenter notes
that in the SOCAL proposed rule, NMFS
sets its threshold for temporary hearing
loss and behavioral effects, or
‘‘temporary threshold shift’’ (‘‘TTS’’), at
183 dB re 1 μPa2·s for harbor seals, 204
dB re 1 μPa2·s for northern elephant
seals, and 206 dB re 1 μPa2·s for
California sea lions (73 FR 60878).
However, the commenter notes, in the
proposed rule for AFAST, NMFS
indicates that the TTS threshold for
pinnipeds is 183 dB re 1 μPa2·s. NMFS
does not explain the difference in
thresholds. The commenter makes the
same comment for the PTS thresholds
(which are 20 dB higher than the TTS
thresholds).
Response: As noted in the SOCAL
proposed rule, the TTS thresholds are
183 dB re 1 FPa2·s for harbor seals (and
closely related species), 204 dB re 1
μPa2·s for northern elephant seals (and
closely related species), and 206 dB re
1 μPa2·s for California sea lions (and
closely related species) (73 FR 60878).
The commenter is correct, in the AFAST
rule, NMFS did not fully explain that all
of the pinnipeds that might be exposed
to MFAS are ‘‘closely related’’ to harbor
seals. Therefore, the 183 dB SEL is the
pinniped threshold applied in AFAST.
The AFAST final rule will be amended
to clarify this issue and be consistent
with the SOCAL final rule. The same
answer applies to the comment about
PTS thresholds.
Comment 29: One commenter stated
that NMFS’ take estimates do not reflect
other non-auditory physiological
impacts, such as from chronic exposure
during development, stress, ship
collisions, and exposure to toxic
chemicals.
Response: The commenter is correct
that the Navy’s estimated take numbers
do not reflect non-auditory
physiological impacts because the
quantitative data necessary to address
those factors in the exposure model do
not exist. However, NMFS
acknowledges that a subset of the
animals that are taken by harassment
will also likely experience non-auditory
physiological effects (stress, etc.) and
these effects are addressed in the
proposed rule (see Stress Responses
section). Regarding toxins, the Navy
concluded that the potential ingestion of
toxins, such as the small amount of
propellant or stimulant remaining in the
spent boosters or on pieces of missile
debris, by marine mammals or fish
species would be remote because of (1)
atmospheric dispersion, (2) the diluting
and neutralizing effects of seawater, and
(3) the relatively small area that could
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potentially be affected. Therefore, the
Navy determined that marine mammals
would not be taken via the ingestion of
toxins and they did not request (nor did
NMFS grant) authorization for take of
marine mammals from toxin ingestion.
Similarly, regarding ship strikes, the
Navy’s EIS indicated that the Navy does
not expect marine mammals to be struck
because of standard operating
procedures to reduce the likelihood of
collisions, to include: (1) Use of
lookouts trained to detect all objects on
the surface of the water (including
marine mammals); (2) reasonable and
prudent actions to avoid the close
interactions of Navy assets and marine
mammals; and (3) maneuvering to keep
away from any observed marine
mammal. Therefore, the Navy did not
request (nor did NMFS grant)
authorization for take of marine
mammals from ship strikes.
Comment 30: The Navy’s exclusive
reliance on energy flux density as its
unit of analysis does not take other
potentially relevant acoustic
characteristics into account. Reflecting
this uncertainty, the Navy should
establish a dual threshold for marine
mammal injury.
Response: NMFS currently uses the
injury threshold recommended by
Southall et al. (2007) for MFAS.
Specifically, NMFS uses the 215-dB SEL
sound exposure level threshold (the
commenter refers to it as energy flux
density level). Southall et al. (2007)
presents a dual threshold for injury,
which also includes a 230-dB peak
pressure level threshold. NMFS
discussed this issue with the Navy early
in the MMPA process and determined
that the 215-dB SEL injury threshold
was the more conservative of the two
thresholds (i.e., the 230-dB peak
pressure threshold occurs much closer
to the source than the 215-dB SEL
threshold) and therefore it was not
necessary to consider the 230-dB peak
pressure threshold further. For example,
an animal will be within the 215-dB
SEL threshold and counted as a take
before it is exposed to the 230-dB
threshold. NMFS concurs with Southall
et al. (2007), which asserts that for an
exposed individual, whichever criterion
is exceeded first, the more
precautionary of the two measures
should be used as the operative injury
criterion.
Comment 31: One commenter asserts
that NMFS disregards data gained from
actual whale mortalities. The
commenter cites to peer-reviewed
literature that indicates that sound
levels at the most likely locations of
beaked whales beached in the Bahamas
strandings run far lower than the Navy’s
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threshold for injury here:
Approximately 150–160 dB re 1 μPa for
50–150 seconds, over the course of the
transit. A further modeling effort,
undertaken in part by the Office of
Naval Research, the commenter states,
suggests that the mean exposure level of
beaked whales, given their likely
distribution in the Bahamas’ Providence
Channels and averaging results from
various assumptions, may have been
lower than 140 dB re 1 μPa. Last the
commenter suggests that when duration
is factored in, evidence would support
a maximum energy level (‘‘EL’’)
threshold for serious injury on the order
of 182 dB re 1 μPa2·s, at least for beaked
whales.
Response: No one knows where the
beaked whales were when they were
first exposed to MFAS in the Bahamas
or the duration of exposure for
individuals (in regards to maximum EL)
and, therefore, we cannot accurately
estimate the received level that triggered
the response that ultimately led to the
stranding. Therefore, NMFS is unable to
quantitatively utilize any data from this
event in the mathematical model
utilized to estimate the number of
animals that will be ‘‘taken’’ incidental
to the Navy’s proposed action. However,
NMFS does not disregard the data. The
proposed rule includes a qualitative
discussion of the Bahamas stranding
and four other strandings that NMFS
and the Navy concur that the operation
of MFAS likely contributed to. These
data illustrate a ‘‘worst case scenario’’ of
the range of potential effects from sonar
and the analysis of these strandings
supports the Navy’s request for
authorization to take 10 individuals of
several species by mortality over the 5yr. period.
Comment 32: One commenter states
that NMFS’ and the Navy’s assessment
of the risk of marine mammal injury and
mortality is astonishingly poor.
Although NMFS briefly discusses
stranding events (73 FR 60859), the
Marine Mammal Protection Act requires
NMFS to fully consider the impacts of
sonar on marine mammals to determine
there is no more than a negligible
impact before issuing an incidental take
authorization.
Response: NMFS disagrees. The
proposed rule contains a detailed
discussion of stranding events (those
that were merely coincident with MFAS
use, as well as those for which the
evidence suggests that MFAS exposure
was a contributing factor), a detailed
discussion of the multiple hypotheses
that describe how acoustically-mediated
or behaviorally-mediated bubble growth
can lead to marine mammal strandings,
as well as a comprehensive discussion
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of the more general potential effects to
marine mammals of MFAS exposure.
NMFS analyses fully considers the
impacts to marine mammals, which
allows us to determine that the specified
activites will have a negligible impact
on the affected species or stocks.
Comment 33: One commenter states:
‘‘NMFS fails to take proper account of
published research on bubble growth in
marine mammals, which separately
indicates the potential for injury and
death at lower [received sound] levels.
According to the best available scientific
evidence, gas bubble growth is the
causal mechanism most consistent with
the observed injuries. NMFS’ argument
to the contrary simply misrepresents the
available literature.’’
Response: The proposed rule
contained a detailed discussion of the
many hypotheses involving both
acoustically-mediated and behaviorallymediated bubble growth. NMFS
concluded that there is not sufficient
evidence to definitively say that any of
these hypotheses accurately describe the
exact mechanism that leads from sonar
exposure to a stranding. Despite the
many theories involving bubble
formation (both as a direct cause of
injury and an indirect cause of
stranding), Southall et al., (2007)
summarizes that scientific disagreement
or complete lack of information exists
regarding the following important
points: (1) Received acoustical exposure
conditions for animals involved in
stranding events; (2) pathological
interpretation of observed lesions in
stranded marine mammals; (3) acoustic
exposure conditions required to induce
such physical trauma directly; (4)
whether noise exposure may cause
behavioral reactions (such as atypical
diving behavior) that secondarily cause
bubble formation and tissue damage;
and (5) the extent the post mortem
artifacts introduced by decomposition
before sampling, handling, freezing, or
necropsy procedures affect
interpretation of observed lesions.
Comment 34: One commenter states
that the calculation of PTS (which is
equated to the onset on injury) is based
on studies of TTS that, as discussed
below, are significantly limited.
Response: NMFS addressed this issue
in response to comments 22, 24, and 27.
Effects Analysis
Comment 35: One commenter asserts
that NMFS does not properly
incorporate the latest available data on
marine mammal population structure
and abundance into its analysis. NMFS’
(and the Navy’s) analysis of marine
mammal distribution, habitat
abundance, population structure and
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ecology contains false, misleading or
outdated assumptions that tend to both
underestimate impacts on species and to
impede consideration of mitigation
measures. Specifically, commenters
point to errors in the reported
abundance of blue whales, Baird’s
beaked whales, and sei whales.
Response: The Navy began drafting
and submitted the SOCAL Range
Complex LOA application to NMFS
prior to wide dissemination of the
NMFS’ 2007 U.S. Pacific Stock
Assessment Reports (SAR). Information
on estimated population size was
obtained from the 2006 SAR and these
numbers were carried forward into the
Proposed Rule. Table 3 of this final rule
shows updated population estimates
based on the both the 2007 and 2008
DRAFT U.S. Pacific SARs. Discussion of
population abundance is for general
review of relative population size since
these estimates can vary every year
based on new survey information, or a
revision of previous statistical analysis
by NMFS. Alternately, for the estimated
density of the affected marine mammal
stocks reported in both the proposed
rule and SOCAL EIS, the Navy used a
different calculation provided by NMFS
Southwest Fisheries Science Center
(SWFSC). SWFSC provided a multi-year
statistical analysis of potential marine
mammal densities stratified on visual
ship sightings from south of Point
Conception, California. The density
estimates used in the impact analysis
described in the Proposed and Final
rule are based on NMFS sighting data
stratified for species specific sightings
only occurring within SOCAL. Sighting
data across a species or stock range,
which can often be much broader than
SOCAL, is used for calculating potential
abundance for that stock in the Pacific
SARs. NMFS feels that this approach to
regional density calculation is more
realistic and scientific given limitations
to at-sea marine mammal surveys.
Unlike the abundance numbers, these
NMFS density estimates were directly
used by the Navy in the model and
analysis that generated the take
estimates shown in table 4 of this final
rule. In short, this error neither caused
NMFS to underestimate impacts nor
impeded consideration of mitigation
measures.
Comment 36: The Navy compiled
table of occurrence of marine mammals
(page 60848 of the proposed rule)
overstates the absence of some species
during certain periods. For example,
both humpback and blue whales are
listed as not occurring November-April,
when in fact lower numbers are present
throughout this time, particularly in the
early and late period of that range. This
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table also cites only one confirmed
sighting of Bryde’s whales in California;
however we observed this species on
two occasions in 2006 at SOAR.
Response: Table 4 was meant to be a
generalized summary of SOCAL marine
mammal presence subject to a number
of caveats. Oceanographic variations
within a season could impact relative
occurrence of certain more migratory
species such as blue whales, humpback
whales, and some dolphin species. The
main purpose of the warm and cold
designations was to indicate if enough
sighting data was available within the
specified time in which to calculate a
species density for use in the impact
analysis. Species-specific densities were
provided to the Navy by NMFS
Southwest Fisheries Science Center
based on best available science derived
from NMFS marine mammal surveys
and are shown in Table 4 of this final
rule (same as table 13 in proposed rule).
Status of Bryde’s whales within SOCAL
is perhaps more accurately defined as
rarely documented and status of blue
and humpback whales would more
accurately be generalized by ‘‘YES less’’.
The extent of this species occurrence
within SOCAL is poorly known,
primarily because morphologically
Bryde’s whales and fin whales are very
similar when observed at sea. At the
time of the Navy’s LOA application and
Proposed Rule, 1993 was the last known
confirmed Bryde’s whale sighting prior
to the unpublished sighting reported by
the commenter. Regardless of the words
used in the generalized Table 4 of the
proposed rule, a low density of Bryde’s
whale, as well as densities for blue and
humpback whales, were incorporated
into the impact analysis.
Comment 37: One commenter states
that preliminary results of recent visualacoustic surveys at SOAR (sponsored by
the Navy) suggest that the population
densities used to calculate takes may
seriously underestimate the number of
individuals to be exposed to MFAS/
HFAS. This is most relevant for Cuvier’s
beaked whales, which (with acoustic
direction from the M3R system) were
among the most frequently encountered
species in surveys conducted in 2007
and 2008. The group sizes of Cuvier’s
beaked whales at SOAR were larger on
average than were reported in the linetransect surveys from which take
estimates were derived, and a minimum
30 unique individuals were photoidentified within a limited area of the
SOAR array in a 5-day period in October
2007 (Falcone et al., submitted).
Response: As discussed in the SOCAL
Monitoring Plan, the Navy already has
a funded marine mammal research
program within SOCAL specifically
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looking at science issues related to
beaked whales. Data collection,
analysis, and reporting are ongoing over
the next few years. The commenter is
referring to preliminary data from this
program that was not available to the
Navy or NMFS at the time of the SOCAL
proposed rule. For the SOCAL EIS and
the proposed rule impact analysis, the
Navy and NMFS used the latest beaked
whale density provided by the NMFS
Southwest Fisheries Science Center as
the best available science as of rule
making publication deadlines. As new
small scale density data becomes
published in peer-review literature, the
Navy will consider this information for
future NEPA documentation. Increased
knowledge of beaked whale distribution
within SOCAL is an important science
gap to be filled. This is the intent of
both the ongoing Navy funded research
and the SOCAL Monitoring Plan.
Therefore while quantitative re-analysis
may not be currently warranted based
on the preliminary unpublished data
collected to date, it is interesting to note
the frequency and visual re-sighting rate
of Cuvier’s beaked whales in an area
that has been subject to Navy operations
for over 40 years.
Comment 38: One commenter states
that there are also a number of marine
mammal populations (e.g., bottlenose
dolphins, short-finned pilot whale,
transient killer whale, and minke whale)
in the Southern California region that,
while not threatened or endangered,
have very low abundance and are
therefore particularly vulnerable to
human impact. They are concerned that
a lack of information has biased NMFS
and the Navy’s effects analysis and thus
the potential risk to these species has
been significantly underestimated. They
cite the most recent NOAA stock
assessments which indicate that the loss
of 0.98 individual short-finned pilot
whales and 5.4 individual minke whales
would compromise survival of those
species, and note that NMFS has
authorized 45 and 126 respective takes
of those whales per year.
Response: The NOAA stock
assessment reports are referring to the
loss, or death, of individuals. The takes
that NMFS is authorizing as part of the
current MMPA process are all Level B
Harassment takes which are not
expected to lead to the loss of any of
these animals. Additionally, though
these species have low abundance, the
animals span the entire West Coast and
beyond. The small numbers of these
animals are not all focused in SOCAL
and they are not experiencing repeated
or regular exposures to sonar. NMFS
does not believe that potential risk to
these species has been underestimated
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and for the reasons discussed in the
Negligible Impact Analysis section, we
have determined that the Navy’s
activities in SOCAL will have a
negligible impact on these species or
stocks.
Comment 39: One commenter is
concerned that by adopting the Navy’s
analysis wholesale—and finding that
the ‘‘there will be few, and more likely
no, impacts’’ on fish—NMFS disregards
relevant scientific literature.
Response: The commenter misquotes
the proposed rule. In the Effects on
Marine Mammal habitat section, after
some discussion, NMFS concludes that
there ‘‘will be few, and more likely no,
impacts on the behavior of fish from
active sonar.’’ NMFS also discusses the
potential for both threshold shifts and
mortality to fish from MFAS, though we
conclude that these impacts would be
short-term (threshold shift) and
insignificant to the population as a
whole in light of natural daily mortality
rates.
Comment 40: One commenter noted
that the migratory range of gray whales
is a well documented part of the SOCAL
Range Complex, and is an area of
specific importance for reproduction for
pregnant females (who are documented
to give birth in the area, and newly
pregnant females transit the area) and
calves, all of who are more vulnerable
to adverse effects and impacts. The
commenter stated that these impacts
need to be included in the rule.
Response: As indicated in the Navy’s
SOCAL EIS and referenced in the
proposed rule, gray whales have a welldefined north-south migratory path that
takes them through SOCAL twice a year,
and they do not spend much time, if
any, feeding within SOCAL. Some
calves are born along the coast of
California, however, most are born in
the shallow protected waters on the
Pacific coast on Baja California from
Morro de Santo Domingo south to Isla
Creciente. These areas are well south of
the SOCAL areas used for the majority
of Navy operations. The potential
impacts to mother-calf pairs from sonar
are specifically discussed in the
Potential Effects of Specified Activities
on Marine Mammals section of the
proposed rule. Given the transient
nature of gray whale inshore mother-calf
occurrence, which is on the order of
hours to a day while moving along a
more inshore migration path through
SOCAL, and in light of the Navy’s
mitigation measures, though some
mother-calf pairs may be behaviorally
disturbed, more severe responses are not
anticipated and NMFS determined that
the take will have a negligible impact on
the stock.
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Comment 41: One commenter felt that
the rule discounts the potential impacts
on beaked whales within SOCAL based
on assumptions that are unfounded. The
first is that strandings are unlikely to
occur because events are not planned
‘‘in a location having a constricted
channel less than 35 miles wide or with
limited egress similar to the Bahamas
(because none exist in the SOCAL Range
Complex)’’ (73 FR 60863). The
commenter notes that sonar-associated
beaked whale mortalities have occurred
in other areas (e.g. the Canary Islands in
2002 and 2004) where such bathymetry
was not present, suggesting this as not
a requisite characteristic for sonarinfluenced strandings. The second is the
observation that unusual strandings
have not been recorded to date in the
region is not an indication that
mortalities have not occurred. Given
that most species of cetaceans sink upon
death, and that most beaked whales
occur in very deep water which would
prevent decomposing carcasses from
eventually refloating, it is highly
unlikely that whales suffering mortal
injury at sea would have been detected.
This is especially true in offshore/island
regions, where there is limited shoreline
throughout much of the operational
area, and much of it is steep or rocky
and not conducive to holding moribund
individuals or carcasses.
Response: The rule does not discount
the potential impacts on beaked whales
from sonar. NMFS specifically
addresses the potential impacts to
beaked whales in the ‘‘Acoustically
Mediated Bubble Growth’’ ,
‘‘Behaviorally Mediated Responses to
MFAS That May Lead to Stranding’’,
‘‘Stranding and Mortality’’, and
‘‘Association Between Mass Stranding
Events and Exposure to MFAS’’ sections
of the proposed rule. Specifically, in
recognition of potential impacts to
beaked whales and the scientific
uncertainty surrounding the exact
mechanisms that lead to strandings, the
Navy requested, and NMFS has
authorized, the mortality of 10 beaked
whales over the course of 5 years in the
unlikely event that a stranding occurs as
a result of Navy training exercises.
Additionally, the commenter is
misrepresenting a piece of text from the
proposed rule—though NMFS points
out that the five factors that contributed
to the stranding in the Bahamas are not
all present in southern California, we do
not say that that alone means strandings
are unlikely to occur. We also further
suggest that caution is recommended
when any of the three environmental
factors are present (constricted
channels, steep bathymetry, or surface
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ducts) in the presence of MFAS and
beaked whales. Also, NMFS does not
ever say that the fact that strandings
have not been recorded to date in the
region is not an indication that
mortalities have not occurred. Rather,
we say ‘‘Though not all dead or injured
animals are expected to end up on the
shore (some may be eaten or float out to
sea), one might expect that if marine
mammals were being harmed by active
sonar with any regularity, more
evidence would have been detected over
the 40-yr period’’ (25 of which, people
have actively been collecting stranding
data).
Comment 42: One commenter asserts
that the Navy’s exposure model fails to
consider the following important points:
• Possible synergistic effects of using
multiple sources in the same exercise,
or the combined effects of multiple
exercises.
• Indirect effects, such as the
potential for mother-calf separation, that
can result from short-term disturbance.
• In assuming animals are evenly
distributed—the magnifying effects of
social structure, whereby impacts on a
single animal within a pod, herd, or
other unit may affect the entire group.
• In assuming that every whale
encountered during subsequent
exercises is essentially a new whale—
the cumulative impacts on the breeding,
feeding, and other activities of species
and stocks.
Response: Though the Navy’s model
does not quantitatively consider the
points listed above (because the
quantitative data necessary to include
those concepts in a mathematical model
do not currently exist), NMFS and the
Navy have qualitatively addressed those
concerns in their effects analyses in the
rule and in the Navy’s EIS.
Comment 43: One commenter stated:
‘‘NMFS does not properly account for
reasonably foreseeable reverberation
effects (as in the Haro Strait incident),
giving no indication that its modeling
sufficiently represents areas in which
the risk of reverberation is greatest.’’
Response: The model does indirectly
incorporate surface-ducting (surface
reverberation), as conditions in the
model are based on nominal conditions
calculated from a generalized digitalized
monthly average. Though the model
does not directly consider
reverberations, these effects are
generally at received levels many orders
of magnitude below those of direct
exposures (as demonstrated in the Haro
Strait analysis associated with bottom
reverberation) and thus contribute
essentially nothing to the cumulative
SEL exposure and would not result in
the exposure of an animal to a higher
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SPL than the direct exposure, which is
already considered by the model.
Additionally, within SOCAL, many of
the modeling areas, defined based on
regional bathymetry, are relatively deep
(>1000 feet) and may not be as
influenced by bottom revelation as the
more shallow Haro Strait.
Comment 44: One commenter stated
that NMFS does not consider the
potential for acute synergistic [indirect]
effects from sonar training. For example,
the agency does not consider the greater
susceptibility to vessel strike of animals
that have been temporarily harassed or
disoriented. The absence of analysis is
particularly glaring in light of the 2004
Nowacek et al. study, which indicates
that mid-frequency sources provoke
surfacing and other behavior in North
Atlantic right whales that increases the
risk of vessel strike.
Response: In the proposed rule,
NMFS refers the reader to a conceptual
framework that illustrates the variety of
avenues of effects that can result from
sonar exposure, to include ‘‘risk prone
behavior’’ resulting somewhat indirectly
from attempting to avoid certain
received levels. Though we consider the
potential for this type of interaction,
NMFS does not include detailed
analysis of potential indirect effects that
have not been empirically
demonstrated. Though Nowacek
showed that right whales responded to
a signal with mid-frequency
components (not an actual MFAS
signal) in a way that appeared likely to
put them at greater risk for ship strike,
we do not have evidence that the
hypothesized sequence of behaviors has
actually led to a ship strike.
Additionally, in general and if affected,
marine mammals may be affected by (or
respond to) sonar in more than one
single way when exposed. However,
when analyzing impacts, NMFS
‘‘counts’’ the most severe response. In
the example given by the commenter,
NMFS considers the overall possibility
of ship strikes resulting from Navy
activities, regardless of whether or not
they would be preceded by a lesser
response.
Comment 45: One commenter asked
how oceanographic conditions (e.g.,
water temperature profiles, water depth,
salinity, etc.) will be factored into the
modeling of received sound levels of
MFAS and underwater detonations.
Which oceanographic data sources will
be used?
Response: The Take Calculation
section of the proposed rule generally
discusses how these and other variables
are factored into the take estimates and
references the Navy’s FEIS for the
SOCAL Range Complex, which contains
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the details of the model and how these
variables are incorporated. Due to the
importance that propagation loss plays
in ASW, the Navy has invested heavily
over the last four to five decades in
measuring and modeling environmental
parameters. The result of this effort is
the following collection of global
databases of environmental parameters
that are accepted as standards for all
Navy modeling efforts:
• Water depth—Digital Bathymetry
Data Base Variable Resolution (DBDBV),
• Sound speed—Generalized
Dynamic Environmental Model (GDEM),
• Bottom loss—Low-Frequency
Bottom Loss (LFBL), Sediment
Thickness Database, and HighFrequency Bottom Loss (HFBL), and
• Wind speed—U.S. Navy Marine
Climatic Atlas of the World.
In terms of predicting potential MFAS
exposure to marine mammals sighted
during Navy training events and in
context of the research goals of the
SOCAL Monitoring Plan, there are a
number of general and classified Navy
models using the databases listed above
and real-world measurements that may
be used to predict likely exposure to
compare with concurrent scientific
observation of marine mammal behavior
conducted under the Monitoring Plan.
General Opposition
Comment 46: The NRDC urged NMFS
to withdraw its proposed rule on
SOCAL and to revise the document
prior to its recirculation for public
comment. They suggested NMFS revisit
its profoundly flawed analysis of
environmental impacts and prescribe
mitigation measures that truly result in
the least practicable adverse impact on
marine species.
Response: NMFS has addressed
specific comments related to the effects
analysis here and the mitigation
measures in the Mitigation
Environmental Assessment. We do not
believe that the analysis is flawed and
we believe that the prescribed measures
will result in the least practicable
adverse impacts on the affected species
or stock. Therefore, NMFS does not
intend to withdraw its rule on SOCAL.
Comment 47: A few commenters
expressed general opposition to Navy
activities and NMFS’ issuance of an
MMPA authorization and presented
several reasons why MFAS was not
necessary.
Response: NMFS appreciates the
commenter’s concern for the marine
mammals that live in the area of the
proposed activities. However, the
MMPA directs NMFS to issue an
incidental take authorization if certain
findings can be made. Under the
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MMPA, NMFS must make the decision
of whether or not to issue an
authorization based on the proposed
action that the applicant submits—the
MMPA does not contain a mechanism
for NMFS to question the need for the
action that the applicant has proposed
(unless the action is illegal). Similarly,
any U.S. citizen (including the Navy)
can request and receive an MMPA
authorization as long as all of the
necessary findings can be made. NMFS
has determined that the Navy training
activities in the SOCAL Range Complex
will have a negligible impact on the
affected species or stocks and, therefore,
we plan to issue the requested MMPA
authorization.
Other
Comment 48: Two commenters voiced
general opposition to the Navy’s
capture, caging, or harnessing of marine
mammals.
Response: The Navy does not intend
to capture marine mammals during
these activities and this rule does not
authorize the capture of marine
mammals.
Comment 49: A few members of the
public submitted comments on the
Navy’s EIS that they did not clearly tie
to the proposed rule.
Response: The purpose of this
comment period was for the public to
provide comments on the proposed rule.
Responses were not provided to
comments on the EIS if their bearing on
the MMPA authorization was not clear.
Comment 50: One commenter noted
that in the second column of 73 FR
60860, NMFS correctly asserts that ‘‘As
discussed in the Bahamas report, there
is no likely association between the
minke whale and spotted dolphin
strandings and the operation of MFAS’’
However, on page 60861, third column
under Association of Strandings and
MFAS, the NMFS incorrectly still lists
these species (minke whale and spotted
dolphin) as associated with MFAS.’’
This is incorrect as NMFS previously
states. The sentence reads, ‘‘Other
species (Stenella coeruleoalba, Kogia
breviceps and Balaenoptera
acutorostrata) have stranded, but in
much lower numbers and less
consistently than beaked whales’’ This
sentence should be removed from the
NMFS’ Final Rule.
Response: NMFS concurs that this
sentence is incorrect in the context of
discussing the 5 strandings associated
with MFAS use and has modified the
final rule.
Comment 51: On the third column of
73 FR 60883, after the last sentence in
this section, another sentence should be
inserted to accurately frame the
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biological distribution for the species
(harbor porpoise) in question. The
harbor porpoise is more commonly
found in near shore water from Central
California north of Point Conception to
Alaska.
Response: The commenter is correct.
To add clarity, though the harbor
porpoise criteria were discussed in the
rule, no harbor porpoises are expected
to be harassed incidental to the SOCAL
action, since SOCAL is outside the
normal range of harbor porpoise
distribution.
Comment 52: The MMC recommends
that NMFS work with the Navy to
prepare an adequate analysis under the
National Environmental Policy Act of
proposed operations at Tanner Bank,
but until such an analysis has been
completed, NMFS withhold
authorization for the taking of marine
mammals at that site. MMC noted that
the biological importance of Tanner
Banks is well documented and any
plans to increase naval activity in that
area should be carefully evaluated and
weighed against the options of
increasing the use of alternative,
existing countermeasure sites or placing
the new minefield site elsewhere where
it would be less likely to have a
significant biological impact.
Response: The Navy adequately
considered alternative minefield sites to
the new minefield site at Tanner Banks.
As discussed in the SOCAL Draft and
Final EIS, the Navy proposed to
establish an offshore shallow water
minefield in the SOCAL Range Complex
to support an overall increased
requirement for mine countermeasure
training. The EIS proposed an increase
in mine warfare training operations at
the existing sites, as well as new sites
based on expanding mine warfare
training requirements in SOCAL
associated with:
• Introduction of the MH–60S
Helicopters (which have a new mine
warfare mission focus),
• Introduction of the Littoral Combat
Ship (LCS),
• Transfer of the Navy’s mine warfare
surface ships to San Diego from other
homeports based on BRAC decision,
and
• Overall increased emphasis on
mine warfare training as a result of
concerns about moored mines
Two existing shallow water
minefields were considered as
alternatives to new proposed sites:
ARPA off La Jolla, California and the
Kingfisher Range northwest of Eel Point
at San Clemente Island. In addition, the
Navy evaluated new sites at Tanner
Banks, offshore of Camp Pendleton, and
off the southern end of San Clemente
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Island. The feasibility of each of these
proposed alternatives were evaluated to
determine if they satisfied the following
environmental, infrastructure, and
operationally-related criteria:
• Provide enough training
opportunities and sites to accommodate
all the various mine warfare training
requirements which may overlap in
time and space.
• Provide the unique oceanographic
characteristics (depths less than 150 feet
and offshore bathymetry with steep
sloping canyons) that is representative
of real world potential mine warfare
operational areas.
• Provide the unique oceanographic
characteristics where shallower water
depths occur in a relatively open ocean
area well away from land masses
thereby offering minimal interference
from civilian activities.
• Provide proximity to existing
undersea ranges to include other mine
warfare and anti-submarine ranges with
complimentary features such that
training opportunities could be
optimized in one area reducing time/
costs/personnel tempo and fuel
(primarily aviation but also fuel costs
for ships).
• Geography that optimizes use of the
SOCAL Range Complex space during
exercises and enhances realism of
training (as compared to any other site)
by providing a mine warfare training
opportunity in the same area where
units would be doing other operations at
the same time as could be expected
while deployed.
The sites off Camp Pendleton and off
San Clemente Islands meet several of
the sighting requirements and were
considered by the Navy. The Tanner
Bank site, however, was found to meet
all five of the necessary environmental,
infrastructure, and operational criteria:
• The new Tanner Bank site ensures
that there would be enough sites to
provide the required increase mine
warfare training by providing a new site
away from the existing sites near San
Clemente Island and offshore of La Jolla
significantly enhancing the availability
of training opportunities for the
expanded mine warfare training
requirements.
• The Tanner Bank site provides a
realistic mine warfare environment that
contains a series of underwater
escarpments, canyons, banks, and sea
mounts. Tanner Bank is the highest
peak of the undersea ridges.
• The proposed site is approximately
90 nautical miles from the California
coastline at San Diego and over 10 miles
from San Clemente Island. This location
is sufficiently distant to ensure minimal
interference from civilian activities.
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• The Tanner Bank site is in
proximity to the existing Southern
California Anti-Submarine Warfare
Range (SOAR) and is within the area
proposed for expansion of the SOAR, as
well as the other ranges available on and
around San Clemente Island Offshore
Range (SCIUR). This location would
allow the co-location of anti-submarine
warfare and mine countermeasures
training thereby optimizing the
undersea warfare training available to a
Strike Group, thereby saving time and
fuel.
• Overall, the geographic location of
the Tanner Bank site would enhance the
quality and realism of training available
in the SOCAL Range Complex.
Significant portions of advanced Strike
Group exercise training activities are
concentrated in the areas southwest of
San Clemente Island; adding a mine
warfare range in this area at Tanner
Banks allows mine warfare training to
be conducted with other training
enhancing realism.
Estimated Take of Marine Mammals
As mentioned previously, with
respect to the MMPA, NMFS’ effects
assessments serve three primary
purposes: (1) To put forth the
permissible methods of taking (i.e.,
Level B Harassment (behavioral
harassment), Level A Harassment
(injury), or mortality, including an
identification of the number and types
of take that could occur by Level A or
B harassment or mortality)) and to
prescribe other means of effecting the
least practicable adverse impact on such
species or stock and its habitat (i.e.,
mitigation); (2) to determine whether
the specified activity will have a
negligible impact on the affected species
or stocks of marine mammals (based on
the likelihood that the activity will
adversely affect the species or stock
through effects on annual rates of
recruitment or survival); (3) to
determine whether the specified activity
will have an unmitigable adverse impact
on the availability of the species or
stock(s) for subsistence uses (however,
there are no subsistence communities
that would be affected in southern
California, so this determination is
inapplicable for this rulemaking); and
(4) to prescribe requirements pertaining
to monitoring and reporting.
In the Estimated Take of Marine
Mammals section of the proposed rule,
NMFS related the potential effects to
marine mammals from MFAS/HFAS
and underwater detonation of
explosives (discussed in the Potential
Effects of Specified Activities on Marine
Mammals Section) to the MMPA
definitions of Level A and Level B
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Harassment and quantified (estimated)
the effects on marine mammals that
could result from the specific activities
that the Navy intends to conduct. The
subsections of this analysis are
discussed individually below.
Definition of Harassment
The Definition of Harassment section
of the proposed rule contained the
definitions of Level A and Level B
Harassments, and a discussion of which
of the previously discussed potential
effects of MFAS/HFAS or explosive
detonations fall into the categories of
Level A Harassment (permanent
threshold shift (PTS), acoustically
mediated bubble growth, behaviorally
mediated bubble growth, and physical
disruption of tissues resulting from
explosive shock wave) or Level B
Harassment (temporary threshold shift
(TTS), acoustic masking and
communication impairment, and
behavioral disturbance rising to the
level of harassment). See 73 FR 60836,
pages 60876–60877. No changes have
been made to the discussion contained
in this section of the proposed rule.
Acoustic Take Criteria
In the Acoustic Take Criteria section
of the proposed rule, NMFS described
the development and application of the
acoustic criteria for both MFAS/HFAS
and explosive detonations. See 73 FR
60836, pages 60877–60883. No changes
have been made to the discussion
contained in this section of the
proposed rule. NMFS has also
summarized the acoustic criteria below.
For MFAS/HFAS, NMFS uses
acoustic criteria for PTS, TTS, and
behavioral harassment.
NMFS’ TTS criteria (which indicate
the received level at which onset TTS
(>6dB) is induced) for MFAS/HFAS are
as follows:
• Cetaceans—195 dB re 1 μPa2-s
(based on mid-frequency cetaceans—no
published data exist on auditory effects
of noise in low or high frequency
cetaceans (Southall et al. (2007))
• Harbor Seals (and closely related
species)—183 dB re 1 μPa2-s
• Northern Elephant Seals (and
closely related species)—204 dB re 1
μPa2-s
• California Sea Lions (and closely
related species)—206 dB re 1 μPa2-s
NMFS uses the following acoustic
criteria for injury (Level A Harassment):
• Cetaceans—215 dB re 1 μPa2-s
(based on mid-frequency cetaceans—no
published data exist on auditory effects
of noise in low or high frequency
cetaceans (Southall et al. (2007))
• Harbor Seals (and closely related
species)—203 dB re 1 μPa2-s
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• Northern Elephant Seals (and
closely related species)—224 dB re 1
μPa2-s
• California Sea Lions (and closely
related species)—226 dB re 1 μPa2-s
For the behavioral harassment
criteria, NMFS uses acoustic risk
functions developed by NMFS, with
input from the Navy, to estimate the
probability of behavioral responses to
MFAS/HFAS (interpreted as the
percentage of the exposed population)
that NMFS would classify as harassment
for the purposes of the MMPA given
exposure to specific received levels of
MFA sonar. See 73 FR 60836, pages
60879–60883.
Table 13 in the proposed rule
summarizes the acoustic criteria for
explosive detonations. See 73 FR 60836,
page 60883.
Estimates of Potential Marine Mammal
Exposures and Authorized Take
Estimating the take that will result
from the proposed activities entails the
following four general steps: (1)
Propagation model estimates animals
exposed to sources at different levels;
(2) further modeling determines number
of exposures to levels indicated in
criteria above (i.e., number of takes); (3)
post-modeling corrections refine
estimates to make them more accurate;
and, (4) mitigation is taken into
consideration. More information
regarding the models used, the
assumptions used in the models, and
the process of estimating take is
available in Appendix F of the Navy’s
SOCAL Range Complex FEIS.
(1) In order to quantify the types of
take described in previous sections that
are predicted to result from the Navy’s
specified activities, the Navy first uses
a sound propagation model that predicts
the number of animals that will be
exposed to a range of levels of pressure
and energy (of the metrics used in the
criteria) from MFAS/HFAS and
explosive detonations based on several
important pieces of information,
including:
• Characteristics of the sound sources
Æ Active sonar source characteristics
include: Source level (with horizontal
and vertical directivity corrections),
source depth, center frequency, source
directivity (horizontal/vertical beam
width and horizontal/vertical steer
direction), and ping spacing.
Æ Explosive source characteristics
include: The net explosive weight
(NEW) of an explosive, the type of
explosive, the detonation depth, number
of successive explosions.
• Transmission loss (in 13
representative environmental provinces
across 8 sonar modeling areas in two
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seasons) based on: water depth; sound
speed variability throughout the water
column (warm season exhibits a weak
surface duct, cold season exhibits a
relatively strong surface duct); bottom
geo-acoustic properties (bathymetry);
and wind speed.
• The estimated density of each
marine mammal species in the SOCAL
Range Complex (see Table 4),
horizontally distributed uniformly and
vertically distributed according to dive
profiles based on field data.
(2) Next, the criteria discussed in the
previous section are applied to the
estimated exposures to predict the
number of exposures that exceed the
criteria, i.e., the number of takes by
Level B Harassment, Level A
Harassment, and mortality.
(3) During the development of the EIS
for the SOCAL Range Complex, NMFS
and the Navy determined that the
output of the model could be made
more realistic by applying postmodeling corrections to account for the
following:
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• Acoustic footprints for active sonar
sources must account for land masses
(by subtracting them out).
• Acoustic footprints for active sonar
sources should not be added
independently, rather, the degree to
which the footprints from multiple
ships participating in the same exercise
would typically overlap needs to be
taken into consideration.
• Acoustic modeling should account
for the maximum number of individuals
of a species that could potentially be
exposed to active sonar within the
course of 1 day or a discreet continuous
sonar event if less than 24 hours.
(4) Mitigation measures are taken into
consideration by NMFS and
adjustments may be applied to the
numbers produced by the Navy’s
modeled estimates. For example, in
some cases the raw modeled numbers of
exposures to levels predicted to result in
Level A Harassment from exposure to
MFAS/HFAS might indicate that 1 blue
whale would be exposed to levels of
active sonar anticipated to result in PTS.
However, a blue whale would need to
be within approximately 10 m of the
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source vessel in order to be exposed to
these levels. Because of the mitigation
measures (watchstanders and shutdown
zone), size of blue whales, and nature of
blue whale behavior, it is highly
unlikely that a blue whale would be
exposed to those levels, and therefore
the Navy would not request
authorization for Level A Harassment of
1 blue whale. Table 6 contains the
Navy’s modeled take estimates and the
number of takes that NMFS is
authorizing in these regulations.
(5) Last, the Navy’s specified activities
have been described based on best
estimates of the number of MFAS/HFAS
hours that the Navy will conduct. The
exact number of hours may vary from
year to year, but will not exceed the 5year total indicated in Table 2 (by
multiplying the yearly estimate by 5) by
more than 10 percent. NMFS estimates
that a 10-percent increase in active
sonar hours would result in
approximately a 10-percent increase in
the number of takes, and we have
considered this possibility in our
analysis.
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Mortality
Evidence from five beaked whale
strandings, all of which have taken
place outside of the SOCAL Range
Complex, and have occurred over
approximately a decade, suggests that
the exposure of beaked whales to midfrequency sonar in the presence of
certain conditions (e.g., multiple units
using tactical sonar, steep bathymetry,
constricted channels, strong surface
ducts, etc.) may result in strandings,
potentially leading to mortality.
Although these physical factors believed
to contribute to the likelihood of beaked
whale strandings are not present in
southern California in the aggregate,
scientific uncertainty exists regarding
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what other factors, or combination of
factors, may contribute to beaked whale
strandings. Accordingly, to allow for
scientific uncertainty regarding
contributing causes of beaked whale
strandings and the exact behavioral or
physiological mechanisms that can lead
to the ultimate physical effects
(stranding and/or death), the Navy has
requested authorization for (and NMFS
is authorizing) take, by injury or
mortality. Although the Navy has
requested take by injury or mortality of
10 beaked whales over the course of the
5-yr regulations, the Navy’s model did
not predict injurious takes of beaked
whales and neither NMFS, nor the Navy
anticipates that marine mammal
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3907
strandings or mortality will result from
the operation of MFAS during Navy
exercises within the SOCAL Range
Complex.
Effects on Marine Mammal Habitat
NMFS’ SOCAL Range Complex
proposed rule included a detailed
section that addressed the effects of the
Navy’s activities on Marine Mammal
Habitat. See 73 FR 60836, pages 60886–
60888. The analysis concluded that the
Navy’s activities would have minimal
effects on fish or invertebrates (in their
roles as food sources for marine
mammals), or water quality in the
SOCAL Range Complex. No changes
have been made to the discussion
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contained in this section of the
proposed rule.
Analysis and Negligible Impact
Determination
Pursuant to NMFS’ regulations
implementing the MMPA, an applicant
is required to estimate the number of
animals that will be ‘‘taken’’ by the
specified activities (i.e., takes by
harassment only, or takes by
harassment, injury, and/or death). This
estimate informs the analysis that NMFS
must perform to determine whether the
activity will have a ‘‘negligible impact’’
on the species or stock. Level B
(behavioral) harassment occurs at the
level of the individual(s) and does not
assume any resulting population-level
consequences, though there are known
avenues through which behavioral
disturbance of individuals can result in
population-level effects (for example:
pink-footed geese (Anser
brachyrhynchus) in undisturbed habitat
gained body mass and had about a 46percent reproductive success compared
with geese in disturbed habitat (being
consistently scared off the fields on
which they were foraging) which did
not gain mass and had a 17-percent
reproductive success). A negligible
impact finding is based on the lack of
likely adverse effects on annual rates of
recruitment or survival (i.e., populationlevel effects). An estimate of the number
of Level B harassment takes, alone, is
not enough information on which to
base an impact determination. In
addition to considering estimates of the
number of marine mammals that might
be ‘‘taken’’ through behavioral
harassment, NMFS must consider other
factors, such as the likely nature of any
responses (their intensity, duration,
etc.), the context of any responses
(critical reproductive time or location,
migration, etc.), or any of the other
variables mentioned in the first
paragraph (if known), as well as the
number and nature of estimated Level A
takes, the number of estimated
mortalities, and effects on habitat.
Generally speaking, and especially with
other factors being equal, the Navy and
NMFS anticipate more severe effects
from takes resulting from exposure to
higher received levels (though this is in
no way a strictly linear relationship
throughout species, individuals, or
circumstances) and less severe effects
from takes resulting from exposure to
lower received levels.
In the Analysis and Negligible Impact
Determination section of the proposed
rule, NMFS addressed the issues
identified in the preceding paragraph in
combination with additional detailed
analysis regarding the severity of the
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anticipated effects, and including
species (or group)-specific discussions,
to determine that Navy activities
utilizing MFAS/HFAS and underwater
detonations will have a negligible
impact on the marine mammal species
and stocks present in the SOCAL Range
Complex. No changes have been made
to the discussion contained in this
section of the proposed rule. See 73 FR
60836, pages 60889–60899.
Subsistence Harvest of Marine
Mammals
NMFS has determined that the
issuance of these regulations and
subsequent LOAs for Navy activities in
the SOCAL Range Complex would not
have an unmitigable adverse impact on
the availability of the affected species or
stocks for taking for subsistence uses,
since there are no such uses in the
specified area.
ESA
There are nine marine mammal
species and four sea turtle species listed
as threatened or endangered under the
ESA with confirmed or possible
occurrence in the study area: Humpback
whale, North Pacific right whale, sei
whale, fin whale, blue whale, sperm
whale, southern resident killer whale,
Guadalupe fur seal, Steller sea lion,
loggerhead sea turtle, the green sea
turtle, leatherback sea turtle, and olive
ridley sea turtle. White Abalone
(Haliotis sorenseni) are also present in
the Navy’s action area. Pursuant to
Section 7 of the ESA, the Navy has
consulted with NMFS on this action.
NMFS has also consulted internally on
the issuance of regulations under
section 101(a)(5)(A) of the MMPA for
this activity. In a Biological Opinion
(BiOp), NMFS concluded that the
Navy’s activities in the SOCAL Range
Complex and NMFS’ issuance of these
regulations are not likely to jeopardize
the continued existence of threatened or
endangered species or destroy or
adversely modify any designated critical
habitat.
NMFS (the Endangered Species
Division) will also issue BiOps and
associated incidental take statements
(ITSs) to NMFS (the Permits,
Conservation, and Recreation Division)
to exempt the take (under the ESA) that
NMFS authorizes in the LOAs under the
MMPA. Because of the difference
between the statutes, it is possible that
ESA analysis of the applicant’s action
could produce a take estimate that is
different than the takes requested by the
applicant (and analyzed for
authorization by NMFS under the
MMPA process), despite the fact that the
same proposed action (i.e. number of
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sonar hours and explosive detonations)
was being analyzed under each statute.
When this occurs, NMFS staff
coordinate to ensure that that the most
conservative (lowest) number of takes
are authorized. For the Navy’s proposed
training in the SOCAL Range Complex,
coordination with the Endangered
Species Division indicates that they will
likely allow for a lower level of take of
ESA-listed marine mammals than were
requested by the applicant (because
their analysis indicates that fewer will
be taken than estimated by the
applicant). Therefore, the number of
authorized takes in NMFS’ LOA(s) will
reflect the lower take numbers from the
ESA consultation, though the specified
activities (i.e., number of sonar hours,
etc.) will remain the same. Alternately,
these regulations indicate the maximum
number of takes that may be authorized
under the MMPA.
The ITS(s) issued for each LOA will
contain implementing terms and
conditions to minimize the effect of the
marine mammal take authorized
through the 2009 LOA (and subsequent
LOAs in 2010, 2011, 2012, and 2013).
With respect to listed marine mammals,
the terms and conditions of the ITSs
will be incorporated into the LOAs.
NEPA
NMFS participated as a cooperating
agency on the Navy’s Final
Environmental Impact Statement (FEIS)
for the Southern California Range
Complex. NMFS subsequently adopted
the Navy’s EIS for the purpose of
complying with the MMPA.
Additionally, NMFS prepared an
Environmental Assessment (EA) that
tiered off the Navy’s FEIS. The EA
analyzed the environmental effects of
several different mitigation alternatives
for the issuance of the SOCAL Range
Complex rule and subsequent LOAs. A
finding of no significant impact for the
mitigation EA was issued in January,
2009.
Determination
Based on the analysis contained
herein and in the proposed rule (and
other related documents) of the likely
effects of the specified activity on
marine mammals and their habitat and
dependent upon the implementation of
the mitigation measures, NMFS finds
that the total taking from Navy training,
maintenance, and RDT&E activities
utilizing MFAS/HFAS and underwater
explosives in the SOCAL Range
Complex over the 5 year period will
have a negligible impact on the affected
species or stocks and will not result in
an unmitigable adverse impact on the
availability of marine mammal species
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or stocks for taking for subsistence uses
because no subsistence uses exist in the
SOCAL Range Complex. NMFS has
issued regulations for these exercises
that prescribe the means of effecting the
least practicable adverse impact on
marine mammals and their habitat and
set forth requirements pertaining to the
monitoring and reporting of that taking.
Classification
This action does not contain a
collection of information requirement
for purposes of the Paperwork
Reduction Act.
Pursuant to the procedures
established to implement section 6 of
Executive Order 12866, the Office of
Management and Budget has
determined that this final rule is
significant.
Pursuant to the Regulatory Flexibility
Act, the Chief Counsel for Regulation of
the Department of Commerce certified at
the proposed rule stage to the Chief
Counsel for Advocacy of the Small
Business Administration that this final
rule, if adopted, would not have a
significant economic impact on a
substantial number of small entities.
The Regulatory Flexibility Act requires
Federal agencies to prepare an analysis
of a rule’s impact on small entities
whenever the agency is required to
publish a notice of proposed
rulemaking. However, a Federal agency
may certify, pursuant to 5 U.S.C. section
605(b), that the action will not have a
significant economic impact on a
substantial number of small entities.
The Navy is the entity that will be
affected by this rulemaking, not a small
governmental jurisdiction, small
organization or small business, as
defined by the Regulatory Flexibility
Act. Any requirements imposed by a
Letter of Authorization issued pursuant
to these regulations, and any monitoring
or reporting requirements imposed by
these regulations, will be applicable
only to the Navy. Because this action, if
adopted, would directly affect the Navy
and not a small entity, NMFS concludes
the action would not result in a
significant economic impact on a
substantial number of small entities.
The Assistant Administrator for
Fisheries has determined that there is
good cause under the Administrative
Procedure Act (5 U.S.C. 553(d)(3)) to
waive the 30-day delay in effective date
of the measures contained in the final
rule. Since January 23, 2007, the Navy
has been conducting military readiness
activities employing mid-frequency
active sonar (MFAS) pursuant to a 2year MMPA National Defense
Exemption (NDE). The NDE served as a
bridge to long-term compliance with the
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MMPA while the Navy prepared its
Environmental Impact Statement and
pursued the necessary MMPA
incidental take authorization for the
SOCAL Range Complex. The NDE will
expire on January 23, 2009, by which
time it is imperative that the regulations
and the measures identified in a
subsequent LOA become effective. Any
delay of these measures would result in
either: (1) A suspension of ongoing or
planned naval exercises, which would
disrupt vital sequential training and
certification processes essential to
national security; or (2) the Navy’s noncompliance with the MMPA (should the
Navy conduct exercises without an
LOA), thereby resulting in the potential
for unauthorized takes of marine
mammals upon expiration of the NDE.
National security and NMFS’ and
Navy’s preference that the Navy be in
compliance with the MMPA after
January 23, 2009, dictate that these
measures go into effect immediately.
The Navy is the entity subject to the
regulations and has informed NMFS
that it is imperative that these measures
be effective on or before January 23,
2009. Finally, as recognized by the
President when issuing the Presidential
Exemption under the CZMA for the
SOCAL COMPTUEX/JTFEX exercises,
the training proposed to be conducted
in SOCAL is in the paramount interest
of the United States. Also, the Supreme
Court noted SOCAL is an ideal location
for conducting integrated training
exercises as the only area on the west
coast that is relatively close to land, air
and sea bases as well as amphibious
landings areas. Any delay in the
implementation of these measures
would raise serious national security
implications. Therefore, these measures
will become effective upon filing.
List of Subjects in 50 CFR Part 216
Exports, Fish, Imports, Incidental
take, Indians, Labeling, Marine
mammals, Navy, Penalties, Reporting
and recordkeeping requirements,
Seafood, Sonar, Transportation.
Dated: January 14, 2009.
Samuel D. Rauch III,
Deputy Administrator for Regulatory
Programs, National Marine Fisheries Service.
For reasons set forth in the preamble,
50 CFR Part 216 is amended as follows:
■
PART 216—REGULATIONS
GOVERNING THE TAKING AND
IMPORTING OF MARINE MAMMALS
1. The authority citation for part 216
continues to read as follows:
■
Authority: 16 U.S.C. 1361 et seq.
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2. Subpart X is added to part 216 to
read as follows:
■
Subpart X—Taking Marine Mammals
Incidental to U.S. Navy Training in the
Southern California Range Complex
Sec.
216.270 Specified activity and specified
geographical region.
216.271 Effective dates and definitions.
216.272 Permissible methods of taking.
216.273 Prohibitions.
216.274 Mitigation.
216.275 Requirements for monitoring and
reporting.
216.276 Applications for Letters of
Authorization.
216.277 Letters of Authorization.
216.278 Renewal of Letters of
Authorization.
216.279 Modifications to Letters of
Authorization.
Subpart X—Taking Marine Mammals
Incidental to U.S. Navy Training in the
Southern California Range Complex
(SOCAL Range Complex)
§ 216.270 Specified activity and specified
geographical region.
(a) Regulations in this subpart apply
only to the U.S. Navy for the taking of
marine mammals that occurs in the area
outlined in paragraph (b) of this section
and that occurs incidental to the
activities described in paragraph (c) of
this section.
(b) The taking of marine mammals by
the Navy is only authorized if it occurs
within the SOCAL Range Complex (as
depicted in Figure ES–1 in the Navy’s
Final Environmental Impact Statement
for the SOCAL Range Complex), which
extends southwest from southern
California in an approximately 700 by
200 nm rectangle with the seaward
corners at 27°30′00″ N. lat.; 127°10′04″
W. long. and 24°00′01″ N. lat.;
125°00′03″ W. long.
(c) The taking of marine mammals by
the Navy is only authorized if it occurs
incidental to the following activities
within the designated amounts of use:
(1) The use of the following midfrequency active sonar (MFAS) sources,
high frequency active sonar (HFAS)
sources for U.S. Navy anti-submarine
warfare (ASW), mine warfare (MIW)
training, maintenance, or research,
development, testing, and evaluation
(RDT&E) in the amounts indicated
below (+/¥10 percent):
(i) AN/SQS–53 (hull-mounted active
sonar)—up to 9885 hours over the
course of 5 years (an average of
1977 hours per year)
(ii) AN/SQS–56 (hull-mounted active
sonar)—up to 2470 hours over the
course of 5 years (an average of 494
hours per year)
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(iii) AN/BQQ–10 (submarine active
sonar)—up to 4075 hours over the
course of 5 years (an average of 815
hours per year)(an average of 2
pings per hour during training
events, 60 pings per hour for
maintenance)
(iv) AN/AQS–22 or 13 (active helicopter
dipping sonar)—up to 13595 dips
over the course of 5 years (an
average of 2719 dips per year—10
pings per dip)
(v) SSQ–62 (Directional Command
Activated Sonobuoy System
(DICASS) sonobuoys)—up to 21275
sonobuoys over the course of 5
years (an average of 4255 sonobuoys
per year)
(vi) MK–48 (heavyweight torpedoes)—
up to 435 torpedoes over the course
of 5 years (an average of 87
torpedoes per year)
(vii) AN/BQQ–15 (submarine
navigational sonar)—up to 610
hours over the course of 5 years (an
average of 122 hours per year)
(viii) MK–46 (lightweight torpedoes)—
up to 420 torpedoes over the course
of 5 years (an average of 84
torpedoes per year)
(ix) AN/SLQ–25A NIXIE—up to 1135
hours over the course of 5 years (an
average of 227 hours per year)
(x) AN/SSQ–125 (AEER sonar
sonobuoy)—up to 540 sonobuoys
(total, of EER/IEER and AEER) over
the course of 5 years (an average of
108 per year))
(2) The detonation of the underwater
explosives identified in paragraph
(c)(2)(i) conducted as part of the training
exercises identified in paragraph
(c)(2)(ii):
(i) Underwater Explosives:
(A) 5’’ Naval Gunfire (9.5 lbs)
(B) 76 mm rounds (1.6 lbs)
(C) Maverick (78.5 lbs)
(D) Harpoon (448 lbs)
(E) MK–82 (238 lbs)
(F) MK–83 (574 lbs)
(G) MK–84 (945 lbs)
(H) MK–48 (851 lbs)
(I) Demolition Charges (20 lbs)
(J) AN/SSQ–110A (IEER explosive
sonobuoy—5 lbs)
(ii) Training Events:
(A) Surface-to-surface Gunnery
Exercises (S–S GUNEX)—up to
2010 exercises over the course of 5
years (an average of 402 per year)
(B) Air-to-surface Missile Exercises
(A-S MISSILEX)—up to 250
exercises over the course of 5 years
(an average of 50 per year)
(C) Bombing Exercises (BOMBEX)—
up to 200 exercises over the course
of 5 years (an average of 40 per
year)
(D) Sinking Exercises (SINKEX)—up
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to 10 exercises over the course of 5
years (an average of 2 per year)
(E) Extended Echo Ranging and
Improved Extended Echo Ranging
(EER/IEER) Systems—up to 15
exercises (total, of EER/IEER and
AEER combined) over the course of
5 years (an average of 3 exercises,
or 108 sonobuoy deployments, per
year).
§ 216.271
Effective dates and definitions.
(a) Regulations are effective January
14, 2009 through January 14, 2014.
(b) The following definitions are
utilized in these regulations:
(1) Uncommon Stranding Event
(USE)—A stranding event that takes
place during an integrated, coordinated,
or major training exercise (MTE) and
involves any one of the following:
(i) Two or more individuals of any
cetacean species (not including mother/
calf pairs, unless of species of concern
listed in § 216.271(b)(1)(ii) found dead
or live on shore within a two day period
and occurring within 30 miles of one
another.
(ii) A single individual or mother/calf
pair of any of the following marine
mammals of concern: Beaked whale of
any species, dwarf or pygmy sperm
whales, short-finned pilot whales,
humpback whales, sperm whales, blue
whales, fin whales, or sei whales.
(iii) A group of 2 or more cetaceans
of any species exhibiting indicators of
distress as defined in the SOCAL Range
Complex Stranding Response Plan.
(2) Shutdown—The cessation of
MFAS/HFAS operation or detonation of
explosives within 14 nm of any live, in
the water, animal involved in a USE.
§ 216.272
Permissible methods of taking.
(a) Under Letters of Authorization
issued pursuant to §§ 216.106 and
216.277, the Holder of the Letter of
Authorization may incidentally, but not
intentionally, take marine mammals
within the area described in
§ 216.270(b), provided the activity is in
compliance with all terms, conditions,
and requirements of these regulations
and the appropriate Letter of
Authorization.
(b) The activities identified in
§ 216.270(c) must be conducted in a
manner that minimizes, to the greatest
extent practicable, any adverse impacts
on marine mammals and their habitat.
(c) The incidental take of marine
mammals under the activities identified
in § 216.270(c) is limited to the
following species, by the indicated
method of take and the indicated
number of times:
(1) Level B Harassment (+/¥10
percent of the number of takes indicated
below):
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(i) Mysticetes:
(A) Humpback whale (Megaptera
novaeangliae)—110 (an average of
22 annually)
(B) Fin whale (Balaenoptera
physalus)—870 (an average of 174
annually)
(C) Blue whale (Balaenoptera
musculus)—3085 (an average of 617
annually)
(D) Minke whale (Balaenoptera
acutorostrata)—665 (an average of
133 annually)
(E) Gray whale (Eschrichtius
robustus)—27340 (an average of
5468 annually)
(ii) Odontocetes:
(A) Sperm whales (Physeter
macrocephalus)—775 (an average of
155 annually)
(B) Pygmy sperm whales (Kogia
breviceps)—830 (an average of 166
annually)
(C) Dwarf sperm whale (Kogia sima)—
100 (an average of 20 annually)
(D) Mesoplodont beaked whales
(Blainville’s, Hubb’s, Perrin’s,
pygmy, and ginkgo-toothed)
(Mesoplodon densirostris, M.
carlhubbsi, M. perrini, M.
peruvianus, M. ginkgodens)—690
(an average of 138 annually)
(E) Cuvier’s beaked whales (Ziphius
cavirostris)—2175 (an average of
435 annually)
(F) Baird’s beaked whales (Berardius
bairdii)—100 (an average of 20
annually)
(G) Unidentified beaked whales—555
(an average of 104 annually)
(H) Rough-toothed dolphin (Steno
bredanensis)—100 (an average of 20
annually)
(I) Bottlenose dolphin (Tursiops
truncatus)—7480 (an average of
1516 annually)
(J) Pan-tropical spotted dolphin
(Stenella attenuata)—100 (an
average of 20 annually)
(K) Spinner dolphin (Stenella
longirostris)—100 (an average of 20
annually)
(L) Striped dolphin (Stenella
coeruleoalba)—9190 (an average of
1838 annually)
(M) Long-beaked common dolphin
(Delphinus capensis)—23145 (an
average of 4629 annually)
(N) Risso’s dolphin (Grampus
griseus)—17995 (an average of 3599
annually)
(O) Northern right whale dolphin
(Lissodelphis borealis)—7935 (an
average of 1547 annually)
(P) Pacific white-sided dolphin
(Lagenorhynchus obliquidens)—
7020 (an average of 1404 annually)
(Q) Short-beaked common dolphin
(Delphinus delphis)—197350 (an
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average of 39470 annually)
(R) Melon-headed whale
(Peponocephala electra)—100 (an
average of 20 annually)
(S) Pygmy killer whale (Feresa
attenuata)—100 (an average of 20
annually)
(T) False killer whale (Pseudorca
crassidens)—100 (an average of 20
annually)
(U) Killer whale (Orcinus orca)—70
(an average of 14 annually)
(V) Short-finned pilot whale
(Globicephala macrorynchus)—260
(an average of 52 annually)
(W) Dall’s porpoise (Phocoenoides
dalli)—3145 (an average of 629
annually)
(iii) Pinnipeds:
(A) Northern elephant seal (Mirounga
angustirostris)—4795 (an average of
959 annually)
(B) Pacific harbor seal (Phoca
vitulina)—28380 (an average of
5676 annually)
(C) California sea lion (Zalophus
californianus)—277530 (an average
of 55506 annually)
(D) Northern fur seal (Callorhinus
ursinus)—6185 (an average of 1237
annually)
(E) Guadalupe fur seal (Arctocephalus
townsendi)—5340 (an average of
1068 annually)
(2) Level A Harassment and/or
mortality of no more than 10 beaked
whales (total), of any of the species
listed in § 216.272(c)(1)(ii)(D) through
(G) over the course of the 5-year
regulations.
jlentini on PROD1PC65 with RULES5
§ 216.273
Prohibitions.
Notwithstanding takings
contemplated in § 216.272 and
authorized by a Letter of Authorization
issued under §§ 216.106 and 216.277,
no person in connection with the
activities described in § 216.270 may:
(a) Take any marine mammal not
specified in § 216.272(c);
(b) Take any marine mammal
specified in § 216.272(c) other than by
incidental take as specified in
§ 216.272(c)(1) and (2);
(c) Take a marine mammal specified
in § 216.272(c) if such taking results in
more than a negligible impact on the
species or stocks of such marine
mammal; or
(d) Violate, or fail to comply with, the
terms, conditions, and requirements of
these regulations or a Letter of
Authorization issued under §§ 216.106
and 216.277.
§ 216.274
Mitigation.
(a) When conducting activities
identified in § 216.270(c), the mitigation
measures contained in the Letter of
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Authorization issued under §§ 216.106
and 216.277 must be implemented.
These mitigation measures include, but
are not limited to:
(1) Navy’s General SOCAL Maritime
Measures for All Training at Sea:
(i) Personnel Training (for all Training
Types):
(A) All commanding officers (COs),
executive officers (XOs), lookouts,
Officers of the Deck (OODs), junior
OODs (JOODs), maritime patrol aircraft
aircrews, and Anti-submarine Warfare
(ASW)/Mine Warfare (MIW) helicopter
crews shall complete the NMFSapproved Marine Species Awareness
Training (MSAT) by viewing the U.S.
Navy MSAT digital versatile disk (DVD).
All bridge lookouts shall complete both
parts one and two of the MSAT; part
two is optional for other personnel.
(B) Navy lookouts shall undertake
extensive training in order to qualify as
a watchstander in accordance with the
Lookout Training Handbook (Naval
Education and Training Command
[NAVEDTRA] 12968–D).
(C) Lookout training shall include onthe-job instruction under the
supervision of a qualified, experienced
lookout. Following successful
completion of this supervised training
period, lookouts shall complete the
Personal Qualification Standard
Program, certifying that they have
demonstrated the necessary skills (such
as detection and reporting of partially
submerged objects). Personnel being
trained as lookouts can be counted
among required lookouts as long as
supervisors monitor their progress and
performance.
(D) Lookouts shall be trained in the
most effective means to ensure quick
and effective communication within the
command structure in order to facilitate
implementation of mitigation measures
if marine species are spotted.
(ii) Operating Procedures and
Collision Avoidance:
(A) Prior to major exercises, a Letter
of Instruction, Mitigation Measures
Message or Environmental Annex to the
Operational Order shall be issued to
further disseminate the personnel
training requirement and general marine
species mitigation measures.
(B) COs shall make use of marine
species detection cues and information
to limit interaction with marine species
to the maximum extent possible
consistent with safety of the ship.
(C) While underway, surface vessels
shall have at least two lookouts with
binoculars; surfaced submarines shall
have at least one lookout with
binoculars. Lookouts already posted for
safety of navigation and man-overboard
precautions may be used to fill this
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3911
requirement. As part of their regular
duties, lookouts will watch for and
report to the OOD the presence of
marine mammals.
(D) On surface vessels equipped with
a mid-frequency active sensor, pedestal
mounted ‘‘Big Eye’’ (20x110) binoculars
shall be properly installed and in good
working order to assist in the detection
of marine mammals in the vicinity of
the vessel.
(E) Personnel on lookout shall employ
visual search procedures employing a
scanning methodology in accordance
with the Lookout Training Handbook
(NAVEDTRA 12968–D).
(F) After sunset and prior to sunrise,
lookouts shall employ Night Lookout
Techniques in accordance with the
Lookout Training Handbook.
(NAVEDTRA 12968–D).
(G) While in transit, naval vessels
shall be alert at all times, use extreme
caution, and proceed at a ‘‘safe speed’’
so that the vessel can take proper and
effective action to avoid a collision with
any marine animal and can be stopped
within a distance appropriate to the
prevailing circumstances and
conditions.
(H) When marine mammals have been
sighted in the area, Navy vessels shall
increase vigilance and take reasonable
and practicable actions to avoid
collisions and activities that might
result in close interaction of naval assets
and marine mammals. Actions may
include changing speed and/or direction
and are dictated by environmental and
other conditions (e.g., safety, weather).
(I) Floating weeds and kelp, algal
mats, clusters of seabirds, and jellyfish
are good indicators of marine mammals.
Therefore, where these circumstances
are present, the Navy shall exercise
increased vigilance in watching for
marine mammals.
(J) Navy aircraft participating in
exercises at sea shall conduct and
maintain, when operationally feasible
and safe, surveillance for marine
mammals as long as it does not violate
safety constraints or interfere with the
accomplishment of primary operational
duties. Marine mammal detections shall
be immediately reported to assigned
Aircraft Control Unit for further
dissemination to ships in the vicinity of
the marine species as appropriate when
it is reasonable to conclude that the
course of the ship will likely result in
a closing of the distance to the detected
marine mammal.
(K) All vessels shall maintain logs and
records documenting training
operations should they be required for
event reconstruction purposes. Logs and
records will be kept for a period of 30
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days following completion of a major
training exercise.
(2) Navy’s Measures for MFAS
Operations:
(i) Personnel Training (for MFAS
Operations):
(A) All lookouts onboard platforms
involved in ASW training events shall
review the NMFS-approved Marine
Species Awareness Training material
prior to use of mid-frequency active
sonar.
(B) All COs, XOs, and officers
standing watch on the bridge shall have
reviewed the Marine Species Awareness
Training material prior to a training
event employing the use of midfrequency active sonar.
(C) Navy lookouts shall undertake
extensive training in order to qualify as
a watchstander in accordance with the
Lookout Training Handbook (Naval
Educational Training [NAVEDTRA],
12968-D).
(D) Lookout training shall include onthe-job instruction under the
supervision of a qualified, experienced
watchstander. Following successful
completion of this supervised training
period, lookouts shall complete the
Personal Qualification Standard
program, certifying that they have
demonstrated the necessary skills (such
as detection and reporting of partially
submerged objects). This does not forbid
personnel being trained as lookouts
from being counted as those listed in
previous measures so long as
supervisors monitor their progress and
performance.
(E) Lookouts shall be trained in the
most effective means to ensure quick
and effective communication within the
command structure in order to facilitate
implementation of mitigation measures
if marine species are spotted.
(ii) Lookout and Watchstander
Responsibilities:
(A) On the bridge of surface ships,
there shall always be at least three
people on watch whose duties include
observing the water surface around the
vessel.
(B) All surface ships participating in
ASW training events shall, in addition
to the three personnel on watch noted
previously, have at all times during the
exercise at least two additional
personnel on watch as marine mammal
lookouts.
(C) Personnel on lookout and officers
on watch on the bridge shall have at
least one set of binoculars available for
each person to aid in the detection of
marine mammals.
(D) On surface vessels equipped with
mid-frequency active sonar, pedestal
mounted ‘‘Big Eye’’ (20x110) binoculars
shall be present and in good working
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order to assist in the detection of marine
mammals in the vicinity of the vessel.
(E) Personnel on lookout shall employ
visual search procedures employing a
scanning methodology in accordance
with the Lookout Training Handbook
(NAVEDTRA 12968–D).
(F) After sunset and prior to sunrise,
lookouts shall employ Night Lookouts
Techniques in accordance with the
Lookout Training Handbook.
(G) Personnel on lookout shall be
responsible for reporting all objects or
anomalies sighted in the water
(regardless of the distance from the
vessel) to the Officer of the Deck, since
any object or disturbance (e.g., trash,
periscope, surface disturbance,
discoloration) in the water may be
indicative of a threat to the vessel and
its crew or indicative of a marine
species that may need to be avoided as
warranted.
(iii) Operating Procedures:
(A) Navy will distribute final
mitigation measures contained in the
LOA and the Incidental take statement
of NMFS’ biological opinion to the
Fleet.
(B) COs shall make use of marine
species detection cues and information
to limit interaction with marine species
to the maximum extent possible
consistent with safety of the ship.
(C) All personnel engaged in passive
acoustic sonar operation (including
aircraft, surface ships, or submarines)
shall monitor for marine mammal
vocalizations and report the detection of
any marine mammal to the appropriate
watch station for dissemination and
appropriate action.
(D) During mid-frequency active sonar
operations, personnel shall utilize all
available sensor and optical systems
(such as night vision goggles) to aid in
the detection of marine mammals.
(E) Navy aircraft participating in
exercises at sea shall conduct and
maintain, when operationally feasible
and safe, surveillance for marine species
of concern as long as it does not violate
safety constraints or interfere with the
accomplishment of primary operational
duties.
(F) Aircraft with deployed sonobuoys
shall use only the passive capability of
sonobuoys when marine mammals are
detected within 200 yds (183 m) of the
sonobuoy.
(G) Marine mammal detections shall
be immediately reported to assigned
Aircraft Control Unit for further
dissemination to ships in the vicinity of
the marine species as appropriate where
it is reasonable to conclude that the
course of the ship will likely result in
a closing of the distance to the detected
marine mammal.
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(H) Safety Zones—When marine
mammals are detected by any means
(aircraft, shipboard lookout, or
acoustically) within or closing to inside
1,000 yds (914 m) of the sonar dome
(the bow), the ship or submarine shall
limit active transmission levels to at
least 6 decibels (dB) below normal
operating levels.
(1) Ships and submarines shall
continue to limit maximum
transmission levels by this 6-dB factor
until the animal has been seen to leave
the area, has not been detected for 30
minutes, or the vessel has transited
more than 2,000 yds (1829 m) beyond
the location of the last detection.
(2) Should a marine mammal be
detected within or closing to inside 500
yds (457 m) of the sonar dome, active
sonar transmissions shall be limited to
at least 10–dB below the equipment’s
normal operating level. Ships and
submarines shall continue to limit
maximum ping levels by this 10–dB
factor until the animal has been seen to
leave the area, has not been detected for
30 minutes, or the vessel has transited
more than 2,000 yds (1829 m) beyond
the location of the last detection.
(3) Should the marine mammal be
detected within or closing to inside 200
yds (183 m) of the sonar dome, active
sonar transmissions shall cease. Sonar
shall not resume until the animal has
been seen to leave the area, has not been
detected for 30 minutes, or the vessel
has transited more than 2,000 yds (1829
m) beyond the location of the last
detection.
(4) Special conditions applicable for
dolphins and porpoises only: If, after
conducting an initial maneuver to avoid
close quarters with dolphins or
porpoises, the OOD concludes that
dolphins or porpoises are deliberately
closing to ride the vessel’s bow wave, no
further mitigation actions are necessary
while the dolphins or porpoises
continue to exhibit bow wave riding
behavior.
(5) If the need for power-down should
arise as detailed in paragraph
(a)(2)(iii)(H) of this section, the Navy
shall follow the requirements as though
they were operating at 235 dB—the
normal operating level (i.e., the first
power-down will be to 229 dB,
regardless of at what level above 235 dB
active sonar was being operated).
(I) Prior to start up or restart of active
sonar, operators will check that the
Safety Zone radius around the sound
source is clear of marine mammals.
(J) Active sonar levels (generally)—
Navy shall operate active sonar at the
lowest practicable level, not to exceed
235 dB, except as required to meet
tactical training objectives.
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(K) Helicopters shall observe/survey
the vicinity of an ASW training event
for 10 minutes before the first
deployment of active (dipping) sonar in
the water.
(L) Helicopters shall not dip their
active sonar within 200 yds (183 m) of
a marine mammal and shall cease
pinging if a marine mammal closes
within 200 yds (183 m) after pinging has
begun.
(M) Submarine sonar operators shall
review detection indicators of closeaboard marine mammals prior to the
commencement of ASW training events
involving active mid-frequency sonar.
(N) Night vision goggles shall be
available to all ships and air crews, for
use as appropriate.
(3) Navy’s Measures for Underwater
Detonations:
(i) Surface-to-Surface Gunnery
(explosive rounds):
(A) Lookouts shall visually survey for
floating weeds and kelp. Intended
impact (i.e., where the Navy is aiming)
shall not be within 600 yds (585 m) of
known or observed floating weeds and
kelp, and algal mats.
(B) For exercises using targets towed
by a vessel or aircraft, target-towing
vessels/aircraft shall maintain a trained
lookout for marine mammals, if
applicable. If a marine mammal is
sighted in the vicinity, the tow aircraft/
vessel shall immediately notify the
firing vessel, which shall suspend the
exercise until the area is clear.
(C) A 600-yard radius buffer zone
shall be established around the intended
target.
(D) From the intended firing position,
trained lookouts shall survey the buffer
zone for marine mammals prior to
commencement and during the exercise
as long as practicable.
(E) The exercise shall be conducted
only when the buffer zone is visible and
marine mammals are not detected
within it.
(ii) Surface-to-Surface Gunnery (nonexplosive rounds):
(A) Lookouts shall visually survey for
floating weeds and kelp, and algal mats.
Intended impact will not be within 200
yds (183 m) of known or observed
floating weeds and kelp, and algal mats.
(B) A 200-yd (183 m) radius buffer
zone shall be established around the
intended target.
(C) From the intended firing position,
trained lookouts shall survey the buffer
zone for marine mammals prior to
commencement and during the exercise
as long as practicable.
(D) If applicable, target towing vessels
shall maintain a lookout. If a marine
mammal is sighted in the vicinity of the
exercise, the tow vessel shall
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immediately notify the firing vessel in
order to secure gunnery firing until the
area is clear.
(E) The exercise shall be conducted
only when the buffer zone is visible and
marine mammals are not detected
within the target area and the buffer
zone.
(iii) Surface-to-Air Gunnery
(explosive and non-explosive rounds):
(A) Vessels shall orient the geometry
of gunnery exercises in order to prevent
debris from falling in the area of sighted
marine mammals.
(B) Vessels will expedite the recovery
of any parachute deploying aerial targets
to reduce the potential for entanglement
of marine mammals.
(C) Target towing aircraft shall
maintain a lookout, if applicable. If a
marine mammal is sighted in the
vicinity of the exercise, the tow aircraft
shall immediately notify the firing
vessel in order to secure gunnery firing
until the area is clear.
(iv) Air-to-Surface Gunnery (explosive
and non-explosive rounds)
(A) If surface vessels are involved,
lookouts will visually survey for floating
kelp in the target area. Impact shall not
occur within 200 yds (183 m) of known
or observed floating weeds and kelp or
algal mats.
(B) A 200 yd (183 m) radius buffer
zone shall be established around the
intended target.
(C) If surface vessels are involved,
lookout(s) shall visually survey the
buffer zone for marine mammals prior to
and during the exercise.
(D) Aerial surveillance of the buffer
zone for marine mammals shall be
conducted prior to commencement of
the exercise. Aircraft crew/pilot shall
maintain visual watch during exercises.
Release of ordnance through cloud
cover is prohibited: aircraft must be able
to actually see ordnance impact areas.
(E) The exercise shall be conducted
only if marine mammals are not visible
within the buffer zone.
(v) Small Arms Training—(grenades,
explosive and non-explosive rounds)—
Lookouts will visually survey for
floating weeds or kelp, algal mats, and
marine mammals. Weapons shall not be
fired in the direction of known or
observed floating weeds or kelp, algal
mats, or marine mammals.
(vi) Air-to-Surface At-sea Bombing
Exercises (explosive and non-explosive):
(A) If surface vessels are involved,
trained lookouts shall survey for floating
kelp and marine mammals. Ordnance
shall not be targeted to impact within
1,000 yds (914 m) of known or observed
floating kelp or marine mammals.
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(B) A 1,000 yd (914 m) radius buffer
zone shall be established around the
intended target.
(C) Aircraft shall visually survey the
target and buffer zone for marine
mammals prior to and during the
exercise. The survey of the impact area
shall be made by flying at 1,500 ft (152
m) or lower, if safe to do so, and at the
slowest safe speed. Release of ordnance
through cloud cover is prohibited:
aircraft must be able to actually see
ordnance impact areas. Survey aircraft
should employ most effective search
tactics and capabilities.
(D) The exercise will be conducted
only if marine mammals are not visible
within the buffer zone.
(vii) Air-to-Surface Missile Exercises
(explosive and non-explosive):
(A) Ordnance shall not be targeted to
impact within 1,800 yds (1646 m) of
known or observed floating kelp.
(B) Aircraft shall visually survey the
target area for marine mammals. Visual
inspection of the target area shall be
made by flying at 1,500 (457 m) feet or
lower, if safe to do so, and at slowest
safe speed. Firing or range clearance
aircraft must be able to actually see
ordnance impact areas. Explosive
ordnance shall not be targeted to impact
within 1,800 yds (1646 m) of sighted
marine mammals.
(viii) Demolitions, Mine Warfare, and
Mine Countermeasures (up to a 20-lb
NEW charge):
(A) Exclusion Zones—All
Demolitions, Mine Warfare and Mine
Countermeasures Operations involving
the use of explosive charges must
include exclusion zones for marine
mammals to prevent physical and/or
acoustic effects to those species. These
exclusion zones shall extend in a 700yard arc radius around the detonation
site.
(B) Pre-Exercise Surveys—For
Demolition and Ship Mine
Countermeasures Operations, preexercise survey shall be conducted
within 30 minutes prior to the
commencement of the scheduled
explosive event. The survey may be
conducted from the surface, by divers,
and/or from the air, and personnel shall
be alert to the presence of any marine
mammal. Should a marine mammal be
present within the survey area, the
exercise shall be paused until the
animal voluntarily leaves the area. The
Navy shall suspend detonation exercises
and ensure the area is clear for a full 30
minutes prior to detonation. Personnel
shall record any marine mammal
observations during the exercise.
(C) Post-Exercise Surveys—Surveys
within the same radius shall also be
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conducted within 30 minutes after the
completion of the explosive event.
(D) Reporting—If there is evidence
that a marine mammal may have been
stranded, injured or killed by the action,
Navy activities shall be immediately
suspended and the situation
immediately reported by the
participating unit to the Officer in
Charge of the Exercise (OCE), who will
follow Navy procedures for reporting
the incident to Commander, Pacific
Fleet, Commander, Third Fleet,
Commander, Navy Region Southwest,
Environmental Director, and the chainof-command. The situation shall also be
reported to NMFS (see Stranding Plan
for details).
(ix) Mining Operations—Initial target
points shall be briefly surveyed prior to
inert ordnance (no live ordnance used)
release from an aircraft to ensure the
intended drop area is clear of marine
mammals. To the extent feasible, the
Navy shall retrieve inert mine shapes
dropped during Mining Operations.
(x) Sink Exercise:
(A) All weapons firing shall be
conducted during the period 1 hour
after official sunrise to 30 minutes
before official sunset.
(B) An exclusion zone with a radius
of 1.5 nm shall be established around
each target. This 1.5 nm zone includes
a buffer of 0.5 nm to account for errors,
target drift, and animal movement. In
addition to the 1.5 nm exclusion zone,
a further safety zone, which extends
from the exclusion zone at 1.5 nm out
an additional 0.5 nm, shall be surveyed.
Together, the zones (exclusion and
safety) extend out 2 nm from the target.
(C) A series of surveillance overflights shall be conducted within the
exclusion and the safety zones, prior to
and during the exercise, when feasible.
Survey protocol shall be as follows:
(1) Overflights within the exclusion
zone shall be conducted in a manner
that optimizes the surface area of the
water observed. This may be
accomplished through the use of the
Navy’s Search and Rescue Tactical Aid,
which provides the best search altitude,
ground speed, and track spacing for the
discovery of small, possibly dark objects
in the water based on the environmental
conditions of the day. These
environmental conditions include the
angle of sun inclination, amount of
daylight, cloud cover, visibility, and sea
state.
(2) All visual surveillance activities
shall be conducted by Navy personnel
trained in visual surveillance. At least
one member of the mitigation team shall
have completed the Navy’s marine
mammal training program for lookouts.
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(3) In addition to the overflights, the
exclusion zone shall be monitored by
passive acoustic means, when assets are
available. This passive acoustic
monitoring would be maintained
throughout the exercise. Potential assets
include sonobuoys, which can be
utilized to detect any vocalizing marine
mammals (particularly sperm whales) in
the vicinity of the exercise. The
sonobuoys shall be re-seeded as
necessary throughout the exercise.
Additionally, passive sonar onboard
submarines may be utilized to detect
any vocalizing marine mammals in the
area. The OCE would be informed of
any aural detection of marine mammals
and would include this information in
the determination of when it is safe to
commence the exercise.
(4) On each day of the exercise, aerial
surveillance of the exclusion and safety
zones shall commence 2 hours prior to
the first firing.
(5) The results of all visual, aerial, and
acoustic searches shall be reported
immediately to the OCE. No weapons
launches or firing may commence until
the OCE declares the safety and
exclusion zones free of marine
mammals.
(6) If a protected species observed
within the exclusion zone is diving,
firing shall be delayed until the animal
is re-sighted outside the exclusion zone,
or 30 minutes have elapsed. After 30
minutes, if the animal has not been resighted it would be assumed to have left
the exclusion zone.
(7) During breaks in the exercise of 30
minutes or more, the exclusion zone
shall again be surveyed for any
protected species. If marine mammals
are sighted within the exclusion zone,
the OCE shall be notified, and the
procedure described in paragraph
(a)(3)(x)(C)(6 ) of this section would be
followed.
(8) Upon sinking of the vessel, a final
surveillance of the exclusion zone shall
be monitored for 2 hours, or until
sunset, to verify that no marine
mammals were harmed.
(D) Aerial surveillance shall be
conducted using helicopters or other
aircraft based on necessity and
availability. The Navy has several types
of aircraft capable of performing this
task; however, not all types are available
for every exercise. For each exercise, the
available asset best suited for
identifying objects on and near the
surface of the ocean would be used.
These aircraft would be capable of
flying at the slow safe speeds necessary
to enable viewing of marine vertebrates
with unobstructed, or minimally
obstructed, downward and outward
visibility. The exclusion and safety zone
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surveys may be cancelled in the event
that a mechanical problem, emergency
search and rescue, or other similar and
unexpected event preempts the use of
one of the aircraft onsite for the
exercise.
(E) Where practicable, the Navy shall
conduct the exercise in sea states that
are ideal for marine mammal sighting,
i.e., Beaufort Sea State 3 or less. In the
event of a 4 or above, survey efforts
shall be increased within the zones.
This shall be accomplished through the
use of an additional aircraft, if available,
and conducting tight search patterns.
(F) The exercise shall not be
conducted unless the exclusion zone
can be adequately monitored visually.
(G) In the event that any marine
mammals are observed to be harmed in
the area, a detailed description of the
animal shall be taken, the location
noted, and if possible, photos taken.
This information shall be provided to
NMFS via the Navy’s regional
environmental coordinator for purposes
of identification (see the Stranding Plan
for detail).
(H) An after action report detailing the
exercise’s time line, the time the surveys
commenced and terminated, amount,
and types of all ordnance expended, and
the results of survey efforts for each
event shall be submitted to NMFS.
(xi) Extended Echo Ranging/Improved
Extended Echo Ranging (EER/IEER/
AEER):
(A) Crews shall conduct visual
reconnaissance of the drop area prior to
laying their intended sonobuoy pattern.
This search shall be conducted at an
altitude below 457 m (500 yd) at a slow
speed, if operationally feasible and
weather conditions permit. In dual
aircraft operations, crews are allowed to
conduct coordinated area clearances.
(B) For IEER (AN/SSQ–110A), crews
shall conduct a minimum of 30 minutes
of visual and aural monitoring of the
search area prior to commanding the
first post detonation. This 30-minute
observation period may include pattern
deployment time.
(C) For any part of the briefed pattern
where a post (source/receiver sonobuoy
pair) will be deployed within 914 m
(1,000 yd) of observed marine mammal
activity, the Navy shall deploy the
receiver ONLY and monitor while
conducting a visual search. When
marine mammals are no longer detected
within 914 m (1,000 yd) of the intended
post position, the Navy shall co-locate
the explosive source sonobuoy (AN/
SSQ–110A) (source) with the receiver.
(D) When able, Navy crews shall
conduct continuous visual and aural
monitoring of marine mammal activity.
This is to include monitoring of own-
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aircraft sensors from first sensor
placement to checking off station and
out of RF range of these sensors.
(E) Aural Detection—If the presence
of marine mammals is detected aurally,
then that shall cue the Navy aircrew to
increase the diligence of their visual
surveillance. Subsequently, if no marine
mammals are visually detected, then the
crew may continue multi-static active
search.
(F) Visual Detection—If marine
mammals are visually detected within
914 m (1,000 yd) of the explosive source
sonobuoy (AN/SSQ–110A) intended for
use, then that payload shall not be
detonated. Aircrews may utilize this
post once the marine mammals have not
been re-sighted for 30 minutes, or are
observed to have moved outside the 914
m (1,000 yd) safety buffer. Aircrews may
shift their multi-static active search to
another post, where marine mammals
are outside the 914 m (1,000 yd) safety
buffer.
(G) For IEER (AN/SSQ–110A),
aircrews shall make every attempt to
manually detonate the unexploded
charges at each post in the pattern prior
to departing the operations area by
using the ‘‘Payload 1 Release’’ command
followed by the ‘‘Payload 2 Release’’
command. Aircrews shall refrain from
using the ‘‘Scuttle’’ command when two
payloads remain at a given post.
Aircrews will ensure that a 914 m (1,000
yd) safety buffer, visually clear of
marine mammals, is maintained around
each post as is done during active
search operations.
(H) Aircrews shall only leave posts
with unexploded charges in the event of
a sonobuoy malfunction, an aircraft
system malfunction, or when an aircraft
must immediately depart the area due to
issues such as fuel constraints,
inclement weather, and in-flight
emergencies. In these cases, the
sonobuoy will self-scuttle using the
secondary or tertiary method.
(I) The Navy shall ensure all payloads
are accounted for. Explosive source
sonobuoys (AN/SSQ–110A) that can not
be scuttled shall be reported as
unexploded ordnance via voice
communications while airborne, then
upon landing via naval message.
(J) Marine mammal monitoring shall
continue until out of own-aircraft sensor
range.
(4) The Navy shall abide by the letter
of the ‘‘Stranding Response Plan for
Major Navy Training Exercises in the
SOCAL Range Complex’’ (available at:
https://www.nmfs.noaa.gov/pr/permits/
incidental.htm), which is incorporated
herein by reference, to include the
following measures:
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(i) Shutdown Procedures—When an
Uncommon Stranding Event (USE—
defined in § 216.271) occurs during a
Major Training Exercise (MTE) (as
defined in the Stranding Plan, meaning
including Sustainment, SHAREM, IAC2,
JTFEX, or COMPTUEX) in the SOCAL
Range Complex, the Navy shall
implement the procedures described
below.
(A) The Navy shall implement a
Shutdown (as defined § 216.271) when
advised by a NMFS Office of Protected
Resources Headquarters Senior Official
designated in the SOCAL Range
Complex Stranding Communication
Protocol that a USE involving live
animals has been identified and that at
least one live animal is located in the
water. NMFS and Navy shall
communicate, as needed, regarding the
identification of the USE and the
potential need to implement shutdown
procedures.
(B) Any shutdown in a given area
shall remain in effect in that area until
NMFS advises the Navy that the
subject(s) of the USE at that area die or
are euthanized, or that all live animals
involved in the USE at that area have
left the area (either of their own volition
or herded).
(C) If the Navy finds an injured or
dead marine mammal floating at sea
during an MTE, the Navy shall notify
NMFS immediately or as soon as
operational security considerations
allow. The Navy shall provide NMFS
with species or description of the
animal(s), the condition of the animal(s)
including carcass condition if the
animal(s) is/are dead), location, time of
first discovery, observed behaviors (if
alive), and photo or video (if available).
Based on the information provided,
NMFS shall determine if, and advise the
Navy whether a modified shutdown is
appropriate on a case-by-case basis.
(D) In the event, following a USE,
that: (a) Qualified individuals are
attempting to herd animals back out to
the open ocean and animals are not
willing to leave, or (b) animals are seen
repeatedly heading for the open ocean
but turning back to shore, NMFS and
the Navy shall coordinate (including an
investigation of other potential
anthropogenic stressors in the area) to
determine if the proximity of MFAS/
HFAS activities or explosive
detonations, though farther than 14 nm
from the distressed animal(s), is likely
decreasing the likelihood that the
animals return to the open water. If so,
NMFS and the Navy shall further
coordinate to determine what measures
are necessary to further minimize that
likelihood and implement those
measures as appropriate.
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3915
(ii) Within 72 hours of NMFS
notifying the Navy of the presence of a
USE, the Navy shall provide available
information to NMFS (per the SOCAL
Range Complex Communication
Protocol) regarding the location, number
and types of acoustic/explosive sources,
direction and speed of units using
MFAS/HFAS, and marine mammal
sightings information associated with
training activities occurring within
80 nm (148 km) and 72 hours prior to
the USE event. Information not initially
available regarding the 80 nm (148 km),
72 hours, period prior to the event shall
be provided as soon as it becomes
available. The Navy shall provide NMFS
investigative teams with additional
relevant unclassified information as
requested, if available.
(iii) Memorandum of Agreement
(MOA)—The Navy and NMFS shall
develop a MOA, or other mechanism
consistent with federal fiscal law
requirements (and all other applicable
laws), that will establish a framework
whereby the Navy can (and provide the
Navy examples of how they can best)
assist NMFS with stranding
investigations in certain circumstances.
§ 216.275 Requirements for monitoring
and reporting.
(a) As outlined in the SOCAL Range
Complex Stranding Communication
Plan, the Navy must notify NMFS
immediately (or as soon as clearance
procedures allow) if the specified
activity identified in § 216.270(c) is
thought to have resulted in the mortality
or injury of any marine mammals, or in
any take of marine mammals not
identified in § 216.272(c).
(b) The Navy must conduct all
monitoring and required reporting
under the Letter of Authorization,
including abiding by the SOCAL Range
Complex Monitoring Plan.
(c) The Navy shall complete an
Integrated Comprehensive Monitoring
Plan (ICMP) in 2009. This planning and
adaptive management tool shall include:
(1) A method for prioritizing
monitoring projects that clearly
describes the characteristics of a
proposal that factor into its priority.
(2) A method for annually reviewing,
with NMFS, monitoring results, Navy
R&D, and current science to use for
potential modification of mitigation or
monitoring methods.
(3) A detailed description of the
Monitoring Workshop to be convened in
2011 and how and when Navy/NMFS
will subsequently utilize the findings of
the Monitoring Workshop to potentially
modify subsequent monitoring and
mitigation.
(4) An adaptive management plan.
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(5) A method for standardizing data
collection across Range Complexes.
(d) General Notification of Injured or
Dead Marine Mammals—Navy
personnel shall ensure that NMFS
(regional stranding coordinator) is
notified immediately (or as soon as
clearance procedures allow) if an
injured or dead marine mammal is
found during or shortly after, and in the
vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater
explosive detonations. The Navy shall
provide NMFS with species or
description of the animal(s), the
condition of the animal(s) (including
carcass condition if the animal is dead),
location, time of first discovery,
observed behaviors (if alive), and photo
or video (if available). The Navy shall
consult the Stranding Response Plan to
obtain more specific reporting
requirements for specific circumstances.
(e) Annual SOCAL Range Complex
Monitoring Plan Report—The Navy
shall submit a report annually on
October 1 describing the
implementation and results (through
August 1 of the same year) of the
SOCAL Range Complex Monitoring
Plan. Data collection methods will be
standardized across range complexes to
allow for comparison in different
geographic locations. Although
additional information will also be
gathered, the marine mammal observers
(MMOs) collecting marine mammal data
pursuant to the SOCAL Range Complex
Monitoring Plan shall, at a minimum,
provide the same marine mammal
observation data required in the data
required in § 216.275(f)(1). The SOCAL
Range Complex Monitoring Plan Report
may be provided to NMFS within a
larger report that includes the required
Monitoring Plan Reports from multiple
Range Complexes.
(f) Annual SOCAL Range Complex
Exercise Report—The Navy shall submit
an Annual SOCAL Range Complex
Exercise Report on October 1 of every
year (covering data gathered through
August 1 of the same year). This report
shall contain information identified in
§ 216.275(f)(1) through (5).
(1) MFAS/HFAS Major Training
Exercises—This section shall contain
the following information for Integrated,
Coordinated, and Major Training
Exercises (MTEs), which include Ship
ASW Readiness and Evaluation
Measuring (SHAREM), Sustainment
Exercises, Integrated ASW Course Phase
II (IAC2), Composite Training Unit
Exercises (COMPTUEX), and Joint Task
Force Exercises (JTFEX) conducted in
the SOCAL Range Complex:
(i) Exercise Information (for each MTE):
(A) Exercise designator
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(B) Date that exercise began and
ended
(C) Location
(D) Number and types of active
sources used in the exercise
(E) Number and types of passive
acoustic sources used in exercise
(F) Number and types of vessels,
aircraft, etc., participating in
exercise
(G) Total hours of observation by
watchstanders
(H) Total hours of all active sonar
source operation
(I) Total hours of each active sonar
source (along with explanation of
how hours are calculated for
sources typically quantified in
alternate way (buoys, torpedoes,
etc.)).
(J) Wave height (high, low, and
average during exercise)
(ii) Individual marine mammal sighting
info (for each sighting in each MTE)
(A) Location of sighting
(B) Species (if not possible—
indication of whale/dolphin/
pinniped)
(C) Number of individuals
(D) Calves observed (y/n)
(E) Initial Detection Sensor
(F) Indication of specific type of
platform observation made from
(including, for example, what type
of surface vessel, i.e., FFG, DDG, or
CG)
(G) Length of time observers
maintained visual contact with
marine mammal
(H) Wave height (in feet)
(I) Visibility
(J) Sonar source in use (y/n).
(K) Indication of whether animal is
< 200 yd, 200–500 yd, 500–1000 yd,
1000–2000 yd, or > 2000 yd from
sonar source in paragraph
(f)(1)(ii)(J) of this section.
(L) Mitigation Implementation—
Whether operation of sonar sensor
was delayed, or sonar was powered
or shut down, and how long the
delay was.
(M) If source in use (i.e., in paragraph
(f)(1)(ii)(J) of this section) is hullmounted, true bearing of animal
from ship, true direction of ship’s
travel, and estimation of animal’s
motion relative to ship (opening,
closing, parallel)
(N) Observed behavior—
Watchstanders shall report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animals (such as
animal closing to bow ride,
paralleling course/speed, floating
on surface and not swimming, etc.)
(iii) An evaluation (based on data
gathered during all of the MTEs) of
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the effectiveness of mitigation
measures designed to avoid
exposing marine mammals to midfrequency sonar. This evaluation
shall identify the specific
observations that support any
conclusions the Navy reaches about
the effectiveness of the mitigation.
(2) ASW Summary—This section
shall include the following information
as summarized from both MTEs and
non-major training exercises (unit-level
exercises, such as TRACKEXs):
(i) Total annual hours of each type of
sonar source (along with explanation of
how hours are calculated for sources
typically quantified in alternate way
(buoys, torpedoes, etc.))
(ii) Cumulative Impact Report—To the
extent practicable, the Navy, in
coordination with NMFS, shall develop
and implement a method of annually
reporting non-major (i.e., other than
MTEs) training exercises utilizing hullmounted sonar. The report shall present
an annual (and seasonal, where
practicable) depiction of non-major
training exercises geographically across
the SOCAL Range Complex. The Navy
shall include (in the SOCAL Range
Complex annual report) a brief annual
progress update on the status of the
development of an effective and
unclassified method to report this
information until an agreed-upon (with
NMFS) method has been developed and
implemented.
(3) SINKEXs—This section shall
include the following information for
each SINKEX completed that year:
(i) Exercise information (gathered for
each SINKEX):
(A) Location
(B) Date and time exercise began and
ended
(C) Total hours of observation by
watchstanders before, during, and
after exercise
(D) Total number and types of rounds
expended / explosives detonated
(E) Number and types of passive
acoustic sources used in exercise
(F) Total hours of passive acoustic
search time
(G) Number and types of vessels,
aircraft, etc., participating in
exercise
(H) Wave height in feet (high, low and
average during exercise)
(I) Narrative description of sensors
and platforms utilized for marine
mammal detection and timeline
illustrating how marine mammal
detection was conducted
(ii) Individual marine mammal
observation (by Navy lookouts)
information (gathered for each
marine mammal sighting)
(A) Location of sighting
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(B) Species (if not possible, indicate
whale, dolphin or pinniped)
(C) Number of individuals
(D) Whether calves were observed
(E) Initial detection sensor
(F) Length of time observers
maintained visual contact with
marine mammal
(G) Wave height
(H) Visibility
(I) Whether sighting was before,
during, or after detonations/
exercise, and how many minutes
before or after
(J) Distance of marine mammal from
actual detonations (or target spot if
not yet detonated)—use four
categories to define distance:
(1) The modeled injury threshold
radius for the largest explosive used
in that exercise type in that
OPAREA (738 m for SINKEX in the
SOCAL Range Complex);
(2) The required exclusion zone (1 nm
for SINKEX in the SOCAL Range
Complex);
(3) The required observation distance
(if different than the exclusion zone
(2 nm for SINKEX in the SOCAL
Range Complex); and
(4) Greater than the required observed
distance. For example, in this case,
the observer would indicate if < 738
m, from 738 m to 1 nm, from 1 nm
to 2 nm, and > 2 nm.
(K) Observed behavior—
Watchstanders will report, in plain
language and without trying to
categorize in any way, the observed
behavior of the animal(s) (such as
animal closing to bow ride,
paralleling course/speed, floating
on surface and not swimming etc.),
including speed and direction.
(L) Resulting mitigation
implementation—Indicate whether
explosive detonations were
delayed, ceased, modified, or not
modified due to marine mammal
presence and for how long.
(M) If observation occurs while
explosives are detonating in the
water, indicate munition type in
use at time of marine mammal
detection.
(4) IEER Summary—This section shall
include an annual summary of the
following IEER information:
(i) Total number of IEER events
conducted in the SOCAL Range
Complex
(ii) Total expended/detonated rounds
(buoys)
(iii) Total number of self-scuttled
IEER rounds
(5) Explosives Summary—To the
extent practicable, the Navy will
provide the information described
below for all of their explosive
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exercises. Until the Navy is able to
report in full the information below,
they will provide an annual update
on the Navy’s explosive tracking
methods, including improvements
from the previous year.
(i) Total annual number of each type
of explosive exercises (of those
identified as part of the ‘‘specified
activity’’ in this final rule)
conducted in the SOCAL Range
Complex.
(ii) Total annual expended/detonated
rounds (missiles, bombs, etc.) for
each explosive type.
(g) Sonar Exercise Notification—The
Navy shall submit to the NMFS
Office of Protected Resources
(specific contact information to be
provided in LOA) either an
electronic (preferably) or verbal
report within fifteen calendar days
after the completion of any MTE
(Sustainment, IAC2, SHAREM,
COMPTUEX, or JTFEX) indicating:
(1) Location of the exercise
(2) Beginning and end dates of the
exercise
(3) Type of exercise (e.g., SHAREM,
JTFEX, etc.)
(h) SOCAL Range Complex 5-yr
Comprehensive Report—The Navy
shall submit to NMFS a draft report
that analyzes and summarizes all of
the multi-year marine mammal
information gathered during ASW
and explosive exercises for which
annual reports are required (Annual
SOCAL Range Complex Exercise
Reports and SOCAL Range Complex
Monitoring Plan Reports). This
report will be submitted at the end
of the fourth year of the rule
(November 2012), covering
activities that have occurred
through June 1, 2012
(i) Comprehensive National ASW
Report—By June, 2014, the Navy
shall submit a draft National Report
that analyzes, compares, and
summarizes the active sonar data
gathered (through January 1, 2014)
from the watchstanders and
pursuant to the implementation of
the Monitoring Plans for the SOCAL
Range Complex, the Atlantic Fleet
Active Sonar Training, the HRC, the
Marianas Range Complex, the
Northwest Training Range, the Gulf
of Alaska, and the East Coast
Undersea Warfare Training Range.
(j) The Navy shall respond to NMFS
comments and requests for
additional information or
clarification on the SOCAL Range
Complex Comprehensive Report,
the Comprehensive National ASW
report, the Annual SOCAL Range
Complex Exercise Report, or the
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3917
Annual SOCAL Range Complex
Monitoring Plan Report (or the
multi-Range Complex Annual
Monitoring Plan Report, if that is
how the Navy chooses to submit the
information) if submitted within 3
months of receipt. These reports
will be considered final after the
Navy has addressed NMFS’
comments or provided the
requested information, or three
months after the submittal of the
draft if NMFS does not comment by
then.
(k) In 2011, the Navy shall convene a
Monitoring Workshop in which the
Monitoring Workshop participants
will be asked to review the Navy’s
Monitoring Plans and monitoring
results and make individual
recommendations (to the Navy and
NMFS) of ways of improving the
Monitoring Plans. The
recommendations shall be reviewed
by the Navy, in consultation with
NMFS, and modifications to the
Monitoring Plan shall be made, as
appropriate.
§ 216.276 Applications for Letters of
Authorization.
To incidentally take marine mammals
pursuant to the regulations in this
subpart, the U.S. citizen (as defined by
§ 216.103) conducting the activity
identified in § 216.270(c) (the U.S.
Navy) must apply for and obtain either
an initial Letter of Authorization in
accordance with § 216.277 or a renewal
under § 216.278.
§ 216.277
Letters of Authorization.
(a) A Letter of Authorization, unless
suspended or revoked, will be valid for
a period of time not to exceed the period
of validity of this subpart, but must be
renewed annually subject to annual
renewal conditions in § 216.278.
(b) Each Letter of Authorization will
set forth:
(1) Permissible methods of incidental
taking;
(2) Means of effecting the least
practicable adverse impact on the
species, its habitat, and on the
availability of the species for
subsistence uses (i.e., mitigation); and
(3) Requirements for mitigation,
monitoring and reporting.
(c) Issuance and renewal of the Letter
of Authorization will be based on a
determination that the total number of
marine mammals taken by the activity
as a whole will have no more than a
negligible impact on the affected species
or stock of marine mammal(s).
E:\FR\FM\21JAR5.SGM
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Federal Register / Vol. 74, No. 12 / Wednesday, January 21, 2009 / Rules and Regulations
§ 216.278 Renewal of Letters of
Authorization and Adaptive Management.
jlentini on PROD1PC65 with RULES5
(a) A Letter of Authorization issued
under § 216.106 and § 216.277 for the
activity identified in § 216.270(c) will be
renewed annually upon:
(1) Notification to NMFS that the
activity described in the application
submitted under § 216.276 will be
undertaken and that there will not be a
substantial modification to the
described work, mitigation or
monitoring undertaken during the
upcoming 12 months;
(2) Timely receipt (by the dates
indicated in these regulations) of the
monitoring reports required under
§ 216.275(c) through (j); and
(3) A determination by the NMFS that
the mitigation, monitoring and reporting
measures required under § 216.274 and
the Letter of Authorization issued under
§§ 216.106 and 216.277, were
undertaken and will be undertaken
during the upcoming annual period of
validity of a renewed Letter of
Authorization.
(b) If a request for a renewal of a
Letter of Authorization issued under
§§ 216.106 and 216.278 indicates that a
substantial modification, as determined
by NMFS, to the described work,
mitigation or monitoring undertaken
during the upcoming season will occur,
the NMFS will provide the public a
period of 30 days for review and
comment on the request. Review and
comment on renewals of Letters of
Authorization are restricted to:
(1) New cited information and data
indicating that the determinations made
VerDate Nov<24>2008
19:31 Jan 16, 2009
Jkt 217001
in this document are in need of
reconsideration, and
(2) Proposed changes to the mitigation
and monitoring requirements contained
in these regulations or in the current
Letter of Authorization.
(c) A notice of issuance or denial of
a renewal of a Letter of Authorization
will be published in the Federal
Register.
(d) NMFS, in response to new
information and in consultation with
the Navy, may modify the mitigation or
monitoring measures in subsequent
LOAs if doing so creates a reasonable
likelihood of more effectively
accomplishing the goals of mitigation
and monitoring set forth in the preamble
of these regulations. Below are some of
the possible sources of new data that
could contribute to the decision to
modify the mitigation or monitoring
measures:
(1) Results from the Navy’s
monitoring from the previous year
(either from the SOCAL Range Complex
or other locations).
(2) Findings of the Monitoring
Workshop that the Navy will convene in
2011 (§ 216.275(l)).
(3) Compiled results of Navy funded
research and development (R&D) studies
(presented pursuant to the ICMP
(§ 216.275(d)).
(4) Results from specific stranding
investigations (either from the SOCAL
Range Complex or other locations, and
involving coincident MFAS/HFAS or
explosives training or not involving
coincident use).
PO 00000
Frm 00038
Fmt 4701
Sfmt 4700
(5) Results from the Long Term
Prospective Study described in the
preamble to these regulations.
(6) Results from general marine
mammal and sound research (funded by
the Navy (described below) or
otherwise).
§ 216.279 Modifications to Letters of
Authorization.
(a) Except as provided in paragraph
(b) of this section, no substantive
modification (including withdrawal or
suspension) to the Letter of
Authorization by NMFS, issued
pursuant to §§ 216.106 and 216.277 and
subject to the provisions of this subpart
shall be made until after notification
and an opportunity for public comment
has been provided. For purposes of this
paragraph, a renewal of a Letter of
Authorization under § 216.278, without
modification (except for the period of
validity), is not considered a substantive
modification.
(b) If the Assistant Administrator
determines that an emergency exists
that poses a significant risk to the wellbeing of the species or stocks of marine
mammals specified in § 216.272(c), a
Letter of Authorization issued pursuant
to §§ 216.106 and 216.277 may be
substantively modified without prior
notification and an opportunity for
public comment. Notification will be
published in the Federal Register
within 30 days subsequent to the action.
[FR Doc. E9–1073 Filed 1–14–09; 4:15 pm]
BILLING CODE 3510–22–P
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Agencies
[Federal Register Volume 74, Number 12 (Wednesday, January 21, 2009)]
[Rules and Regulations]
[Pages 3882-3918]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-1073]
[[Page 3881]]
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Part V
Department of Commerce
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National Oceanic and Atmospheric Administration
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50 CFR Part 216
Taking and Importing Marine Mammals; U.S. Navy Training in the Southern
California Range Complex; Final Rule
Federal Register / Vol. 74, No. 12 / Wednesday, January 21, 2009 /
Rules and Regulations
[[Page 3882]]
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DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
50 CFR Part 216
[Docket No. 0808061069-81583-02]
RIN 0648-AW91
Taking and Importing Marine Mammals; U.S. Navy Training in the
Southern California Range Complex
AGENCY: National Marine Fisheries Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA), Commerce.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: NMFS, upon application from the U.S. Navy (Navy), is issuing
regulations to govern the unintentional taking of marine mammals
incidental to training, maintenance, and research, development, testing
and evaluation (RDT&E) activities conducted in the Southern California
Range Complex (SOCAL Range Complex), which extends south and southwest
off the southern California coast, for the period of January 2009
through January 2014. The Navy's activities are considered military
readiness activities pursuant to the Marine Mammal Protection Act
(MMPA), as amended by the National Defense Authorization Act for Fiscal
Year 2004 (NDAA). These regulations, which allow for the issuance of
``Letters of Authorization'' (LOAs) for the incidental take of marine
mammals during the described activities and specified timeframes,
prescribe the permissible methods of taking and other means of
affecting the least practicable adverse impact on marine mammal species
and their habitat, as well as requirements pertaining to the monitoring
and reporting of such taking.
DATES: Effective January 14, 2009 through January 14, 2014.
ADDRESSES: A copy of the Navy's application (which contains a list of
the references used in this document), NMFS' Record of Decision (ROD),
and other documents cited herein, may be obtained by writing to Michael
Payne, Chief, Permits, Conservation and Education Division, Office of
Protected Resources, National Marine Fisheries Service, 1315 East-West
Highway, Silver Spring, MD 20910-3225 or by telephone via the contact
listed here (see FOR FURTHER INFORMATION CONTACT).
FOR FURTHER INFORMATION CONTACT: Jolie Harrison, Office of Protected
Resources, NMFS, (301) 713-2289, ext. 166.
SUPPLEMENTARY INFORMATION: Extensive supplementary information was
provided in the proposed rule for this activity, which was published in
the Federal Register on Tuesday, October 14, 2008 (73 FR 60836). This
information will not be reprinted here in its entirety; rather, all
sections from the proposed rule will be represented herein and will
contain either a summary of the material presented in the proposed rule
or a note referencing the page(s) in the proposed rule where the
information may be found. Any information that has changed since the
proposed rule was published will be addressed herein. Additionally,
this final rule contains a section that responds to the comments
received during the public comment period.
Background
Sections 101(a)(5)(A) and (D) of the MMPA (16 U.S.C. 1361 et seq.)
direct the Secretary of Commerce (Secretary) to allow, upon request,
the incidental, but not intentional taking of marine mammals by U.S.
citizens who engage in a specified activity (other than commercial
fishing) during periods of not more than five consecutive years each if
certain findings are made and regulations are issued or, if the taking
is limited to harassment and of no more than 1 year, the Secretary
shall issue a notice of proposed authorization for public review.
Authorization shall be granted if NMFS finds that the taking will
have a negligible impact on the species or stock(s), will not have an
unmitigable adverse impact on the availability of the species or
stock(s) for subsistence uses, and if the permissible methods of taking
and requirements pertaining to the mitigation, monitoring and reporting
of such taking are set forth.
NMFS has defined ``negligible impact'' in 50 CFR 216.103 as:
An impact resulting from the specified activity that cannot be
reasonably expected to, and is not reasonably likely to, adversely
affect the species or stock through effects on annual rates of
recruitment or survival.
The NDAA (Pub. L. 108-136) removed the ``small numbers'' and
``specified geographical region'' limitations and amended the
definition of ``harassment'' as it applies to a ``military readiness
activity'' to read as follows (Section 3(18)(B) of the MMPA):
(i) Any act that injures or has the significant potential to
injure a marine mammal or marine mammal stock in the wild [Level A
Harassment]; or
(ii) Any act that disturbs or is likely to disturb a marine
mammal or marine mammal stock in the wild by causing disruption of
natural behavioral patterns, including, but not limited to,
migration, surfacing, nursing, breeding, feeding, or sheltering, to
a point where such behavioral patterns are abandoned or
significantly altered [Level B Harassment].
Summary of Request
On April 1, 2008, NMFS received an application from the Navy
requesting authorization for the take of individuals of 37 species of
marine mammals incidental to upcoming Navy training activities,
maintenance, and research, development, testing, and evaluation (RDT&E)
activities to be conducted within the SOCAL Range Complex, which
extends southwest approximately 600 nm in the general shape of a 200-nm
wide rectangle (see the Navy's application), over the course of 5
years. These activities are military readiness activities under the
provisions of the NDAA. The Navy states, and NMFS concurs, that these
military readiness activities may incidentally take marine mammals
present within the SOCAL Range Complex by exposing them to sound from
mid-frequency or high frequency active sonar (MFAS/HFAS) or underwater
detonations. The Navy requests authorization to take individuals of 37
species of marine mammals by Level B Harassment. Further, though they
do not anticipate it to occur, the Navy requests authorization to take,
by injury or mortality, up to 10 beaked whales over the course of the
5-yr period for which the regulations will be in effect.
Background of Navy Request
The proposed rule contains a description of the Navy's mission,
their responsibilities pursuant to Title 10 of the United States Code,
and the specific purpose and need for the activities for which they
requested incidental take authorization. The description contained in
the proposed rule has not changed. See 73 FR 60836.
Overview of the SOCAL Range Complex
The proposed rule contains an overview of the SOCAL Range Complex
that describes the SOCAL Operational Areas (OPAREAS), the Special Use
Airspaces, San Clemente Island, and the overlap with Point Mugu Sea
Range for certain anti-submarine warfare (ASW) training. The
description contained in the proposed rule has not changed. See 73 FR
60836, page 60837.
Description of the Specified Activities
The proposed rule contains a complete description of the Navy's
specified activities that are covered by these final regulations, and
for which the associated incidental take of marine mammals will be
authorized in the related LOAs. The proposed rule
[[Page 3883]]
describes the nature of the activities involving both mid and high-
frequency active sonar (MFAS and HFAS) and explosive detonations, as
well as the MFAS and HFAS sound sources and explosive types. See 73 FR
60836, pages 60837-60847. The narrative description of the action
contained in the proposed rule has not changed, with the exception of
the change from IEER to AEER described in the paragraph below. Tables
1, 2, and 3 summarize the sonar and explosive exercise types used in
the Navy's activities and hours of sonar operation conducted.
The Navy is developing the Advanced Extended Echo Ranging (AEER)
system as a replacement to the IEER system. AEER would use a new active
sonobuoy (AN/SSQ-125) that utilizes a tonal (or a sonar ping) vice
impulsive (or explosive) sound source as a replacement for the SSQ-110A
(the system used in IEER). AEER will still use the ADAR sonobuoy as the
systems receiver and be deployed by Marine Patrol Aircraft. As AEER is
introduced for Fleet use, IEER will be removed. The same total number
of buoys will be deployed as were presented in the proposed rule, but a
subset of them will be AEER instead of IEER. The small difference in
the number of anticipated marine mammal takes that will result from
this change is indicated in the take table, along with other minor
modifications. This small change in the take numbers did not affect
NMFS' analysis of and conclusions regarding the proposed action.
[GRAPHIC] [TIFF OMITTED] TR21JA09.000
[[Page 3884]]
[GRAPHIC] [TIFF OMITTED] TR21JA09.001
[GRAPHIC] [TIFF OMITTED] TR21JA09.002
Description of Marine Mammals in the Area of the Specified Activities
There are 41 marine mammal species with possible or confirmed
occurrence in the SOCAL Range Complex. Nine marine mammal species
listed as federally endangered under the Endangered Species Act (ESA)
can occur in the SOCAL Range Complex: The humpback whale, North Pacific
right whale, sei whale, fin whale, blue whale, sperm whale, southern
resident killer whale, Guadalupe fur seal, and Steller sea lion. The
proposed rule contains a discussion of three species that are not
considered further in the analysis (southern resident killer whale,
North Pacific right whale, and Steller sea lion) because of their
rarity in the SOCAL Range Complex. With the exception of marine mammal
abundance and Steller sea lion correction discussed below, the
Description of Marine Mammals in the Area of the Specified Activities
in the proposed rule remains unchanged (see 73 FR 60836, pages 60846-
60850).
For this rulemaking and subsequent LOA, NMFS' Southwest Fisheries
Science Center calculated marine mammal density estimates based on
compiled densities from vessel surveys conducted from 1986 to 2005, and
provided it to the Navy as Government Furnished Information (GFI).
These density estimates are included in Table 4 and remain unchanged
from the proposed rule. The proposed rule contains a description of the
methods used to estimate density. During the public comment period for
the proposed rule, several members of the public noted and commented
that the abundance numbers provided for some marine mammal species were
not from the latest NMFS stock assessment reports. Those numbers have
been updated in Table 4, which now includes the abundance estimates
from both the 2007 stock assessment reports and the draft 2008 reports.
This correction did not affect NMFS analysis, as take estimates are
based on density estimates (not abundance estimates), which remain
unchanged from those presented in the proposed rule.
The proposed rule indicated (73 FR 60836, page 60849) that the last
sighting of a Steller sea lion in Southern California was that of a sub
adult male that was briefly on San Miguel Island in 1998. In fact, a
Steller sea lion was sighted in Newport Harbor in April 2008 and a
Steller sea lion (that may have been the same individual) live stranded
in Santa Barbara in the summer of 2008. This correction did not affect
NMFS analysis and, as indicated in the proposed rule, Steller sea lions
are not likely to be present in the action area or taken by the Navy's
specified activities.
[[Page 3885]]
[GRAPHIC] [TIFF OMITTED] TR21JA09.003
A Brief Background on Sound
The proposed rule contains a section that provides a brief
background on the principles of sound that are frequently referred to
in this rulemaking. See 73 FR 60836, pages 60850-60851. This section
also includes a discussion of the functional hearing ranges of the
different groups of marine mammals (by frequency) as well as a
discussion of the two main sound metrics used in NMFS analysis (sound
pressure level (SPL) and sound energy level (SEL)). The information
contained in the proposed rule has not changed.
Potential Effects of Specified Activities on Marine Mammals
With respect to the MMPA, NMFS' effects assessment serves four
primary purposes: (1) To prescribe the permissible methods of taking
(i.e., Level B Harassment (behavioral harassment), Level A Harassment
(injury), or mortality, including an identification of the number and
types of take that could occur by Level A or B harassment or mortality)
and to prescribe other means of affecting the least practicable adverse
impact on such species or stock and its habitat (i.e., mitigation); (2)
to determine whether the specified activity will have a negligible
impact on the affected species or stocks of marine mammals (based on
the likelihood that the activity will adversely affect the species or
stock through effects on annual rates of recruitment or survival); (3)
to determine whether the specified activity will have an unmitigable
adverse impact on the availability of the species or stock(s) for
subsistence uses (however, there are no subsistence communities that
would be affected in the SOCAL Range Complex, so this determination is
inapplicable for this rulemaking); and (4) to prescribe requirements
pertaining to monitoring and reporting.
In the Potential Effects of Specified Activities on Marine Mammals
Section of the proposed rule NMFS included a qualitative discussion of
the different ways that MFAS/HFAS and underwater explosive detonations
may potentially affect marine mammals (some of which NMFS would not
classify as harassment). See 73 FR 60836, pages 60851-60863. Marine
mammals may experience direct physiological effects (such as threshold
shift), acoustic masking, impaired communications, stress responses,
and behavioral disturbance. This section also included a discussion of
some of the suggested explanations for the association between the use
of MFAS and marine mammal strandings (such as behaviorally-mediated
bubble growth) that have been observed a limited number of times in
certain circumstances (the specific events are also described). See 73
FR 60836, pages 60859-60863. The information contained in the Potential
Effects of Specified Activities on Marine Mammals Section from the
proposed rule has not changed, with the exception of the following
sentence. On page 60861, NMFS said ``Other species (Stenella
coeruleoalba, Kogia breviceps and Balaenoptera acutorostrata) have
stranded, but in much lower numbers and less consistently than beaked
whales.'' As a member of the public pointed out, and as NMFS stated on
page 60860 of the proposed rule, there was no likely association
between the minke whale and spotted dolphin strandings referred to and
the operation of MFAS. Therefore, the sentence should read ``Other
species, such as Kogia breviceps, have stranded in association with the
operation of MFAS, but in much lower numbers and less consistently than
beaked whales.''
[[Page 3886]]
Later, in the Estimated Take of Marine Mammals section, NMFS
relates and quantifies the potential effects to marine mammals from
MFAS/HFAS and underwater detonation of explosives discussed here to the
MMPA regulatory definitions of Level A and Level B Harassment. NMFS has
also considered the effects of mortality on these species.
Mitigation
In order to issue an incidental take authorization (ITA) under
Section 101(a)(5)(A) of the MMPA, NMFS must prescribe regulations
setting forth the ``permissible methods of taking pursuant to such
activity, and other means of affecting the least practicable adverse
impact on such species or stock and its habitat, paying particular
attention to rookeries, mating grounds, and areas of similar
significance.'' The NDAA of 2004 amended the MMPA as it relates to
military readiness activities and the incidental take authorization
process such that ``least practicable adverse impact'' shall include
consideration of personnel safety, practicality of implementation, and
impact on the effectiveness of the ``military readiness activity.'' The
SOCAL Range Complex activities described in the proposed rule are
considered military readiness activities.
NMFS reviewed the Navy's proposed SOCAL Range Complex activities
and the proposed SOCAL mitigation measures (which the Navy refers to as
Protective Measures) presented in the Navy's application to determine
whether the activities and mitigation measures were capable of
achieving the least practicable adverse effect on marine mammals. NMFS
determined that further discussion was necessary regarding the
potential relationship between the operation of MFAS/HFAS and marine
mammal strandings.
Any mitigation measure prescribed by NMFS should be known to
accomplish, have a reasonable likelihood of accomplishing (based on
current science), or contribute to the accomplishment of one or more of
the general goals listed below:
(a) Avoidance or minimization of injury or death of marine mammals
wherever possible (goals b, c, and d may contribute to this goal).
(b) A reduction in the numbers of marine mammals (total number or
number at biologically important time or location) exposed to received
levels of MFAS/HFAS, underwater detonations, or other activities
expected to result in the take of marine mammals (this goal may
contribute to a, above, or to reducing harassment takes only).
(c) A reduction in the number of times (total number or number at
biologically important time or location) individuals would be exposed
to received levels of MFAS/HFAS, underwater detonations, or other
activities expected to result in the take of marine mammals (this goal
may contribute to a, above, or to reducing harassment takes only).
(d) A reduction in the intensity of exposures (either total number
or number at biologically important time or location) to received
levels of MFAS/HFAS, underwater detonations, or other activities
expected to result in the take of marine mammals (this goal may
contribute to a, above, or to reducing the severity of harassment takes
only).
(e) A reduction in adverse effects to marine mammal habitat, paying
special attention to the food base, activities that block or limit
passage to or from biologically important areas, permanent destruction
of habitat, or temporary destruction/disturbance of habitat during a
biologically important time.
(f) For monitoring directly related to mitigation--an increase in
the probability of detecting marine mammals, thus allowing for more
effective implementation of the mitigation (shut-down zone, etc.).
NMFS worked with the Navy to identify potential additional
practicable and effective mitigation measures, which included a careful
balancing of the likely benefit of any particular measure to the marine
mammals with the likely effect of that measure on personnel safety,
practicality of implementation, and impact on the ``military-readiness
activity''. NMFS and the Navy developed a Stranding Response Plan to
address the concern listed above.
The Navy's proposed mitigation measures, as well as the Stranding
Response Plan, which is required under these regulations, were
described in detail in the proposed rule (73 FR 60836, pages 60863-
60870). The Navy's measures address personnel training, lookout and
watchstander responsibilities, and operating procedures for activities
using both MFAS/HFAS and explosive detonations. Three modifications
(see below) have been made to the mitigation measures described in the
proposed rule. The final SOCAL Stranding Response Plan, which includes
a shutdown protocol, a stranding investigation plan, and a requirement
for Navy and NMFS to implement an MOA that will establish a framework
whereby the Navy can (and provide the Navy examples of how they can
best) assist NMFS with stranding investigations in certain
circumstances, may be viewed at: https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications. Additionally, the mitigation measures are
included in full in the codified text of the regulations.
The proposed rule (the regulatory text, not the preamble) contained
a measure in which the Navy indicated that ``prior to conducting the
exercise, remotely sensed sea surface temperature maps would be
reviewed. SINKEX shall not be conducted within areas where strong
temperature discontinuities are present, thereby indicating the
existence of oceanographic fronts.'' See 73 FR 60836, page 60904. The
Navy included this measure in the LOA application in error. The removal
of the measure does not change NMFS' analysis and therefore the measure
is not included in the final rule.
The following measure has been added to the Mitigation section of
the regulations: Night vision goggles shall be available to all ships
and air crews for use as appropriate.
Last, the same mitigation measures outlined for the IEER system in
the proposed rule will also be applied to the similar, but newly
described, AEER system.
NMFS has determined that the Navy's proposed mitigation measures
(from the LOA application), along with the Stranding Response Plan (and
when the Adaptive Management (see Adaptive Management below) component
is taken into consideration) are adequate means of effecting the least
practicable adverse impacts on marine mammal species or stocks and
their habitat, paying particular attention to rookeries, mating
grounds, and areas of similar significance, while also considering
personnel safety, practicality of implementation, and impact on the
effectiveness of the military readiness activity. The justification for
this conclusion is discussed in the Mitigation Conclusion section of
the proposed rule. See 73 FR 60836, pages 60870-60871. The Mitigation
Conclusion Section of the proposed rule has not changed. Research and
Conservation Measures for Marine Mammals.
The Navy provides a significant amount of funding and support for
marine research. The Navy provided $26 million in Fiscal Year 2008 and
plans for $22 million in Fiscal Year 2009 to universities, research
institutions, federal laboratories, private companies, and independent
researchers around the world to study marine mammals. Over the past
five years the Navy has funded over $100 million in marine mammal
research.
[[Page 3887]]
The U.S. Navy sponsors seventy percent of all U.S. research concerning
the effects of human-generated sound on marine mammals and 50 percent
of such research conducted worldwide. Major topics of Navy-supported
research include the following:
Better understanding of marine species distribution and
important habitat areas,
Developing methods to detect and monitor marine species
before and during training,
Understanding the effects of sound on marine mammals, sea
turtles, fish, and birds, and
Developing tools to model and estimate potential effects
of sound.
The Navy's Office of Naval Research currently coordinates six
programs that examine the marine environment and are devoted solely to
studying the effects of noise and/or the implementation of technology
tools that will assist the Navy in studying and tracking marine
mammals. The six programs are as follows:
Environmental Consequences of Underwater Sound,
Non-Auditory Biological Effects of Sound on Marine
Mammals,
Effects of Sound on the Marine Environment,
Sensors and Models for Marine Environmental Monitoring,
Effects of Sound on Hearing of Marine Animals, and
Passive Acoustic Detection, Classification, and Tracking
of Marine Mammals.
The Navy has also developed the technical reports referenced within
this document and the SOCAL Range Complex EIS, such as the Marine
Resource Assessments. Furthermore, research cruises by NMFS and by
academic institutions have received funding from the U.S. Navy.
The Navy has sponsored several workshops to evaluate the current
state of knowledge and potential for future acoustic monitoring of
marine mammals. The workshops brought together acoustic experts and
marine biologists from the Navy and other research organizations to
present data and information on current acoustic monitoring research
efforts and to evaluate the potential for incorporating similar
technology and methods on instrumented ranges. However, acoustic
detection, identification, localization, and tracking of individual
animals still requires a significant amount of research effort to be
considered a reliable method for marine mammal monitoring. The Navy
supports research efforts on acoustic monitoring and will continue to
investigate the feasibility of passive acoustics as a potential
mitigation and monitoring tool.
Overall, the Navy will continue to fund ongoing marine mammal
research, and is planning to coordinate long-term monitoring/studies of
marine mammals on various established ranges and operating areas. The
Navy will continue to research and contribute to university/external
research to improve the state of the science regarding marine species
biology and acoustic effects. These efforts include mitigation and
monitoring programs; data sharing with NMFS and via the literature for
research and development efforts.
Long-Term Prospective Study
Apart from this final rule, NMFS, with input and assistance from
the Navy and several other agencies and entities, will perform a
longitudinal observational study of marine mammal strandings to
systematically observe and record the types of pathologies and diseases
and investigate the relationship with potential causal factors (e.g.,
sonar, seismic surveys, weather). The proposed rule contained an
outline of the proposed study (73 FR 60836, pages 60837-60838). No
changes have been made to the longitudinal study as described in the
proposed rule.
Monitoring
In order to issue an ITA for an activity, Section 101(a)(5)(A) of
the MMPA states that NMFS must set forth ``requirements pertaining to
the monitoring and reporting of such taking''. The MMPA implementing
regulations at 50 CFR 216.104 (a)(13) indicate that requests for LOAs
must include the suggested means of accomplishing the necessary
monitoring and reporting that will result in increased knowledge of the
species and of the level of taking or impacts on populations of marine
mammals that are expected to be present.
Monitoring measures prescribed by NMFS should accomplish one or
more of the following general goals:
(a) An increase in the probability of detecting marine mammals,
both within the safety zone (thus allowing for more effective
implementation of the mitigation) and in general to generate more data
to contribute to the effects analyses.
(b) An increase in our understanding of how many marine mammals are
likely to be exposed to levels of MFAS/HFAS (or explosives or other
stimuli) that we associate with specific adverse effects, such as
behavioral harassment, TTS, or PTS.
(c) An increase in our understanding of how marine mammals respond
(behaviorally or physiologically) to MFAS/HFAS (at specific received
levels), explosives, or other stimuli expected to result in take and
how anticipated adverse effects on individuals (in different ways and
to varying degrees) may impact the population, species, or stock
(specifically through effects on annual rates of recruitment or
survival).
(d) An increased knowledge of the affected species.
(e) An increase in our understanding of the effectiveness of
certain mitigation and monitoring measures.
(f) A better understanding and record of the manner in which the
authorized entity complies with the incidental take authorization.
Proposed Monitoring Plan for the SOCAL Range Complex
As NMFS indicated in the proposed rule, the Navy has (with input
from NMFS) fleshed out the details of and made improvements to the
SOCAL Range Complex Marine Mammal and Sea Turtle Monitoring Plan
(Monitoring Plan). Additionally, NMFS and the Navy have incorporated a
recommendation from the public, which recommended the Navy hold a
workshop to discuss the Navy's Monitoring Plan (see Monitoring Workshop
section). The final SOCAL Range Complex Monitoring Plan, which is
summarized below may be viewed at https://www.nmfs.noaa.gov/pr/permits/
incidental.htm#applications. The Navy plans to implement all of the
components of the Monitoring Plan; however, only the marine mammal
components (not the sea turtle components) will be required by the MMPA
regulations and associated LOAs.
The draft Monitoring Plan for the SOCAL Range Complex has been
designed as a collection of focused ``studies'' (described fully in the
SOCAL Range Complex Monitoring Plan) to gather data that will allow the
Navy to address the following questions:
(1) Are marine mammals and sea turtles exposed to MFAS, especially
at levels associated with adverse effects (i.e., based on NMFS'
criteria for behavioral harassment, TTS, or PTS)? If so, at what levels
are they exposed?
(2) If marine mammals and sea turtles are exposed to MFAS in the
SOCAL Range Complex, do they redistribute geographically as a result of
continued exposure? If so, how long does the redistribution last?
(3) If marine mammals and sea turtles are exposed to MFAS, what are
their behavioral responses to various levels?
[[Page 3888]]
(4) What are the behavioral responses of marine mammals and sea
turtles that are exposed to explosives at specific levels?
(5) Is the Navy's suite of mitigation measures for MFAS and
explosives (e.g., PMAP, major exercise measures agreed to by the Navy
through permitting) effective at avoiding TTS, injury, and mortality of
marine mammals and sea turtles?
Data gathered in these studies will be collected by qualified,
professional marine mammal biologists that are experts in their field.
They will use a combination of the following methods to collect data:
Visual Surveys--Vessel and aerial.
Passive Acoustic Monitoring (PAM), including working with
the passive acoustic detection capabilities of Navy's SOAR fixed range.
Marine Mammal Observers (MMOs) on Navy Vessels.
Marine Mammal Tagging.
In the five proposed study designs (all of which cover multiple
years), the above methods will be used separately or in combination to
monitor marine mammals in different combinations before, during, and
after activities utilizing MFAS/HFAS or explosive detonations. Table 5
contains a summary of the monitoring effort that is planned for each
study in each year (effort may vary slightly between years or study
type, but overall effort will remain constant). The SOCAL Range Complex
Monitoring Plan is designed to collect data on all marine mammals and
sea turtles encountered during monitoring studies. However, priority
will be given to ESA-listed species and taxa in which MFAS exposure,
under certain circumstances and strandings have been linked (beaked
whales and other deep-diving species).
[GRAPHIC] [TIFF OMITTED] TR21JA09.004
[[Page 3889]]
Monitoring Workshop
During the public comment period on the SOCAL Range Complex
proposed rule (as well as the Hawaii Range Complex proposed rule), NMFS
received a comment which, in consultation with the Navy, we have chosen
to incorporate into the final rule (in a modified form). One commenter
recommended that a workshop or panel be convened to solicit input on
the monitoring plan from researchers, experts, and other interested
parties. The SOCAL Range Complex proposed rule included an adaptive
management component and both NMFS and the Navy believe that a workshop
would provide a means for Navy and NMFS to consider input from
participants in determining whether or how to modify monitoring
techniques to more effectively accomplish the goals of monitoring set
forth earlier in the document. NMFS and the Navy believe that this
workshop concept is valuable in relation to all of the Range Complexes
and major training exercise rules and LOAs that NMFS is working on with
the Navy at this time, and consequently this single Monitoring Workshop
will be included as a component of all of the rules and LOAs that NMFS
will be processing for the Navy in the next year or so.
The Navy, with guidance and support from NMFS, will convene a
Monitoring Workshop, including marine mammal and acoustic experts as
well as other interested parties, in 2011. The Monitoring Workshop
participants will review the monitoring results from the previous two
years of monitoring pursuant to the SOCAL Range Complex rule as well as
monitoring results from other Navy rules and LOAs (e.g., the Atlantic
Fleet Active Sonar Training, Hawaii Range Complex (HRC), and other
rules). The Monitoring Workshop participants would provide their
individual recommendations to the Navy and NMFS on the monitoring
plan(s) after also considering the current science (including Navy
research and development) and working within the framework of available
resources and feasibility of implementation. NMFS and the Navy would
then analyze the input from the Monitoring Workshop participants and
determine the best way forward from a national perspective. Subsequent
to the Monitoring Workshop, modifications would be applied to
monitoring plans as appropriate.
Integrated Comprehensive Monitoring Program
In addition to the Monitoring Plan for the SOCAL Range Complex, the
Navy will complete the Integrated Comprehensive Monitoring Program
(ICMP) Plan by the end of 2009. The ICMP will provide the overarching
coordination that will support compilation of data from range-specific
monitoring plans (e.g., SOCAL Range Complex plan) as well as Navy
funded research and development (R&D) studies. The ICMP will coordinate
the monitoring program's progress towards meeting its goals and develop
a data management plan. The ICMP will be evaluated annually to provide
a matrix for progress and goals for the following year, and will make
recommendations on adaptive management for refinement and analysis of
the monitoring methods.
The primary objectives of the ICMP are to:
Monitor and assess the effects of Navy activities on
protected species;
Ensure that data collected at multiple locations is
collected in a manner that allows comparison between and among
different geographic locations;
Assess the efficacy and practicality of the monitoring and
mitigation techniques;
Add to the overall knowledge-base of marine species and
the effects of Navy activities on marine species.
The ICMP will be used both as: (1) A planning tool to focus Navy
monitoring priorities (pursuant to ESA/MMPA requirements) across Navy
Range Complexes and Exercises; and (2) an adaptive management tool,
through the consolidation and analysis of the Navy's monitoring and
watchstander data, as well as new information from other Navy programs
(e.g., R&D), and other appropriate newly published information.
In combination with the 2011 Monitoring Workshop and the adaptive
management component of the SOCAL Range Complex rule and the other
planned Navy rules (e.g., AFAST and HRC), the ICMP could potentially
provide a framework for restructuring the monitoring plans and
allocating monitoring effort based on the value of particular specific
monitoring proposals (in terms of the degree to which results would
likely contribute to stated monitoring goals, as well as the likely
technical success of the monitoring based on a review of past
monitoring results) that have been developed through the ICMP
framework, instead of allocating based on maintaining an equal (or
commensurate to effects) distribution of monitoring effort across Range
complexes. For example, if careful prioritization and planning through
the ICMP (which would include a review of both past monitoring results
and current scientific developments) were to show that a large, intense
monitoring effort in Hawaii would likely provide extensive, robust and
much-needed data that could be used to understand the effects of sonar
throughout different geographical areas, it may be appropriate to have
other Range Complexes dedicate money, resources, or staff to the
specific monitoring proposal identified as ``high priority'' by the
Navy and NMFS, in lieu of focusing on smaller, lower priority projects
divided throughout their home Range Complexes.
The ICMP will identify:
A means by which NMFS and the Navy would jointly consider
the previous year's monitoring results and advancing science to
determine if modifications are needed in mitigation or monitoring
measures to better effect the goals laid out in the Mitigation and
Monitoring sections of the SOCAL Range Complex rule.
Guidelines for prioritizing monitoring projects.
If, as a result of the workshop and similar to the example
described in the paragraph above, the Navy and NMFS decide it is
appropriate to restructure the monitoring plans for multiple ranges
such that they are no longer evenly allocated (by Range Complex), but
rather focused on priority monitoring projects that are not necessarily
tied to the geographic area addressed in the rule, the ICMP will be
modified to include a very clear and unclassified record-keeping system
that will allow NMFS and the public to see how each Range Complex/
project is contributing to all of the ongoing monitoring (resources,
effort, money, etc.).
Past Monitoring in the SOCAL Range Complex
The proposed rule contained a detailed review of the previous
marine mammal monitoring conducted in the SOCAL Range Complex, which
was conducted in compliance with the terms and conditions of multiple
biological opinions issued for MFAS activities (73 FR 60836, pages
60873-60875). No changes have been made to the discussion contained in
the proposed rule.
Adaptive Management
The final regulations governing the take of marine mammals
incidental to Navy activities in the SOCAL Range Complex will contain
an adaptive
[[Page 3890]]
management component. Our understanding of the effects of MFAS/HFAS and
explosives on marine mammals is still in its relative infancy, and yet
the science in this field continues to improve. These circumstances
make the inclusion of an adaptive management component both valuable
and necessary within the context of 5-year regulations for activities
that have been associated with marine mammal mortality in certain
circumstances and locations (though not the SOCAL Range Complex). The
use of adaptive management will give NMFS the ability to consider new
data from different sources to determine (in coordination with the
Navy) on an annual basis if mitigation or monitoring measures should be
modified or added (or deleted) if new data suggests that such
modifications are appropriate (or are not appropriate) for subsequent
annual LOAs.
Following are some of the possible sources of applicable data:
Results from the Navy's monitoring from the previous year
(either from the SOCAL Range Complex or other locations).
Findings of the Workshop that the Navy will convene in
2011 to analyze monitoring results to date, review current science, and
recommend modifications, as appropriate to the monitoring protocols to
increase monitoring effectiveness.
Compiled results of Navy funded research and development
(R&D) studies (presented pursuant to the ICMP, which is discussed
elsewhere in this document).
Results from specific stranding investigations (either
from the SOCAL Range Complex or other locations, involving the
coincident MFAS/HFAS of explosives training or not involving the
coincident use).
Results from the Long Term Prospective Study described
below.
Results from general marine mammal and sound research
(funded by the Navy (described below) or otherwise).
Mitigation measures could be modified or added (or deleted) if new
data suggests that such modifications would have (or do not have) a
reasonable likelihood of accomplishing the goals of mitigation laid out
in this final rule and if the measures are practicable. NMFS would also
coordinate with the Navy to modify or add to (or delete) the existing
monitoring requirements if the new data suggest that the addition of
(or deletion of) a particular measure would more effectively accomplish
the goals of monitoring laid out in this final rule. The reporting
requirements associated with this rule are designed to provide NMFS
with monitoring data from the previous year to allow NMFS to consider
the data and issue annual LOAs. NMFS and the Navy will meet annually
(prior to LOA issuance, except in the year of the Monitoring Workshop)
to discuss the monitoring reports, Navy R&D developments, and current
science and whether mitigation or monitoring modifications are
appropriate.
Reporting
In order to issue an ITA for an activity, Section 101(a)(5)(A) of
the MMPA states that NMFS must set forth ``requirements pertaining to
the monitoring and reporting of such taking''. Effective reporting is
critical to ensure compliance with the terms and conditions of an LOA,
and to provide NMFS and the Navy with data of the highest quality based
on the required monitoring.
As NMFS noted in its proposed rule, additional detail has been
added to the reporting requirements since they were outlined in the
proposed rule. The updated reporting requirements are all included
below. A subset of the information provided in the monitoring reports
may be classified and not releasable to the public.
NMFS will work with the Navy to develop tables that allow for
efficient submission of the information required below.
General Notification of Injured or Dead Marine Mammals
Navy personnel will ensure that NMFS (regional stranding
coordinator) is notified immediately (or as soon as operational
security allows) if an injured or dead marine mammal is found during or
shortly after, and in the vicinity of, any Navy training exercise
utilizing MFAS, HFAS, or underwater explosive detonations. The Navy
will provide NMFS with species or description of the animal(s), the
condition of the animal(s) (including carcass condition if the animal
is dead), location, time of first discovery, observed behaviors (if
alive), and photo or video (if available). The Stranding Response Plan
contains more specific reporting requirements for specific
circumstances.
Annual SOCAL Range Complex Monitoring Plan Report
The Navy shall submit a report annually on October 1 describing the
implementation and results (through August 1 of the same year) of the
SOCAL Range Complex Monitoring Plan, described above. Data collection
methods will be standardized across range complexes to allow for
comparison in different geographic locations. Although additional
information will also be gathered, marine mammal observers (MMOs)
collecting marine mammal data pursuant to the SOCAL Range Complex
Monitoring Plan shall, at a minimum, provide the same marine mammal
observation data required in the MFAS/HFAS major Training Exercises
section of the Annual SOCAL Range Complex Exercise Report referenced
below.
The SOCAL Range Complex Monitoring Plan Report may be provided to
NMFS within a larger report that includes the required Monitoring Plan
Reports from multiple Range Complexes.
Annual SOCAL Range Complex Exercise Report
The Navy will submit an Annual SOCAL Range Complex Exercise Report
on October 1 of every year (covering data gathered through August 1).
This report shall contain the subsections and information indicated
below.
MFAS/HFAS Major Training Exercises
This section shall contain the following information for
Integrated, Coordinated, and Major Training Exercises (MTEs), which
include Ship ASW Readiness and Evaluation Measuring (SHAREM),
Sustainment Exercises, Integrated ASW Course Phase II (IAC2), Composite
Training Unit Exercises (COMPTUEX), and Joint Task Force Exercises
(JTFEX) conducted in the SOCAL Range Complex:
(a) Exercise Information (for each MTE):
(i) Exercise designator.
(ii) Date that exercise began and ended.
(iii) Location.
(iv) Number and types of active sources used in the exercise.
(v) Number and types of passive acoustic sources used in exercise.
(vi) Number and types of vessels, aircraft, etc., participating in
exercise.
(vii) Total hours of observation by watchstanders.
(viii) Total hours of all active sonar source operation.
(ix) Total hours of each active sonar source (along with explanation of
how hours are calculated for sources typically quantified in alternate
way (buoys, torpedoes, etc.)).
(x) Wave height (high, low, and average during exercise).
(b) Individual marine mammal sighting info (for each sighting in
each MTE):
[[Page 3891]]
(i) Location of sighting.
(ii) Species (if not possible--indication of whale/dolphin/pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial Detection Sensor.
(vi) Indication of specific type of platform observation made from
(including, for example, what type of surface vessel, i.e., FFG, DDG,
or CG).
(vii) Length of time observers maintained visual contact with marine
mammal(s).
(viii) Wave height (in feet).
(ix) Visibility.
(x) Sonar source in use (y/n).
(xi) Indication of whether animal is <200yd, 200-500yd, 500-1000yd,
1000-2000yd, or >2000yd from sonar source in (x) above.
(xiii) Mitigation Implementation--Whether operation of sonar sensor was
delayed, or sonar was powered or shut down, and how long the delay was.
(xiv) If source in use (x) is hullmounted, true bearing of animal from
ship, true direction of ship's travel, and estimation of animal's
motion relative to ship (opening, closing, parallel).
(xv) Observed behavior--Watchstanders shall report, in plain language
and without trying to categorize in any way, the observed behavior of
the animals (such as animal closing to bow ride, paralleling course/
speed, floating on surface and not swimming, etc.).
(c) An evaluation (based on data gathered during all of the MTEs)
of the effectiveness of mitigation measures designed to avoid exposing
animals to mid-frequency sonar. This evaluation shall identify the
specific observations that support any conclusions the Navy reaches
about the effectiveness of the mitigation.
ASW Summary
This section shall include the following information as summarized
from both MTEs and non-major training exercises (unit-level exercises,
such as TRACKEXs):
(i) Total annual hours of each type of sonar source (along with
explanation of how hours are calculated for sources typically
quantified in alternate way (buoys, torpedoes, etc.)).
(iv) Cumulative Impact Report--To the extent practicable, the Navy,
in coordination with NMFS, shall develop and implement a method of
annually reporting non-major (i.e., other than MTEs) training exercises
utilizing hull-mounted sonar. The report shall present an annual (and
seasonal, where practicable) depiction of non-major training exercises
geographically across the SOCAL Range Complex. The Navy shall include
(in the SOCAL Range Complex annual report) a brief annual progress
update on the status of the development of an effective and
unclassified method to report this information until an agreed-upon
(with NMFS) method has been developed and implemented.
SINKEXs
This section shall include the following information for each
SINKEX completed that year:
(a) Exercise info:
(i) Location.
(ii) Date and time exercise began and ended.
(iii) Total hours of observation by watchstanders before, during, and
after exercise.
(iv) Total number and types of rounds expended/explosives detonated.
(v) Number and types of passive acoustic sources used in exercise.
(vi) Total hours of passive acoustic search time.
(vii) Number and types of vessels, aircraft, etc., participating in
exercise.
(viii) Wave height in feet (high, low and average during exercise).
(ix) Narrative description of sensors and platforms utilized for marine
mammal detection and timeline illustrating how marine mammal detection
was conducted.
(b) Individual marine mammal observation (by Navy lookouts) info:
(i) Location of sighting.
(ii) Species (if not possible--indication of whale/dolphin/pinniped).
(iii) Number of individuals.
(iv) Calves observed (y/n).
(v) Initial detection sensor.
(vi) Length of time observers maintained visual contact with marine
mammal.
(vii) Wave height.
(viii) Visibility.
(ix) Whether sighting was before, during, or after detonations/
exercise, and how many minutes before or after.
(x) Distance of marine mammal from actual detonations (or target spot
if not yet detonated)--use four categories to define distance: (1) The
modeled injury threshold radius for the largest explosive used in that
exercise type in that OPAREA (738 m for SINKEX in the SOCAL Range
Complex); (2) the required exclusion zone (1 nm for SINKEX in SOCAL
Range Complex); (3) the required observation distance (if different
than the exclusion zone (2 nm for SINKEX in SOCAL Range Complex); and
(4) greater than the required observed distance. For example, in this
case, the observer would indicate if < 738 m, from 738 m-1 nm, from 1
nm-2 nm, and > 2 nm.
(xi) Observed behavior--Watchstanders will report, in plain language
and without trying to categorize in any way, the observed behavior of
the animals (such as animal closing to bow ride, paralleling course/
speed, floating on surface and not swimming etc.), including speed and
direction.
(xii) Resulting mitigation implementation--Indicate whether explosive
detonations were delayed, ceased, modified, or not modified due to
marine mammal presence and for how long.
(xiii) If observation occurs while explosives are detonating in the
water, indicate munition type in use at time of marine mammal
detection.
Improved Extended Echo-Ranging System (IEER) and Advanced Extended
Echo-Ranging System (AEER) Summary
This section shall include an annual summary of the following IEER/
AEER information:
(i) Total number of IEER and AEER events conducted in the SOCAL Range
Complex.
(ii) Total expended/detonated rounds (buoys).
(iii) Total number of self-scuttled IEER rounds.
Explosives Summary
The Navy is in the process of improving the methods used to track
explosive use to provide increased granularity. To the extent
practicable, the Navy will provide the information described below for
all of their explosive exercises. Until the Navy is able to report in
full the information below, they will provide an annual update on the
Navy's explosive tracking methods, including improvements from the
previous year.
(i) Total annual number of each type of explosive exercise (of those
identified as part of the ``specified activity'' in this final rule)
conducted in the SOCAL Range Complex.
(ii) Total annual expended/detonated rounds (missiles, bombs, etc.) for
each explosive type.
[[Page 3892]]
Sonar Exercise Notification
The Navy shall submit to the NMFS Office of Protected Resources
(specific contact information to be provided in LOA) either an
electronic (preferably) or verbal report within fifteen calendar days
after the completion of any MTE (Sustainment, IAC2, SHAREM, COMPTUEX,
or JTFEX) indicating:
(1) Location of the exercise.
(2) Beginning and end dates of the exercise.
(3) Type of exercise.
SOCAL Range Complex 5-Yr Comprehensive Report
The Navy shall submit to NMFS a draft report that analyzes and
summarizes all of the multi-year marine mammal information gathered
during ASW and explosive exercises for which annual reports are
required (Annual SOCAL Range Complex Exercise Reports and SOCAL Range
Complex Monitoring Plan Reports). This report will be submitted at the
end of the fourth year of the rule (November 2012), covering activities
that have occurred through June 1, 2012.
Comprehensive National ASW Report
By June, 2014, the Navy shall submit a draft National Report that
analyzes, compares, and summarizes the active sonar data gathered
(through January 1, 2014) from the watchstanders and pursuant to the
implementation of the Monitoring Plans for the SOCAL Range Complex, the
Atlantic Fleet Active Sonar Training, the HRC, the Marianas Range
Complex, the Northwest Training Range, the Gulf of Alaska, and the East
Coast Undersea Warfare Training Range.
The Navy shall respond to NMFS comments and requests for additional
information or clarification on the SOCAL Range Complex Comprehensive
Report, the Comprehensive National ASW report, the Annual SOCAL Range
Complex Exercise Report, or the Annual SOCAL Range Complex Monitoring
Plan Report (or the multi-Range Complex Annual Monitoring Plan Report,
if that is how the Navy chooses to submit the information) if submitted
within 3 months of receipt. These reports will be considered final
after the Navy has addressed NMFS' comments or provided the requested
information, or three months after the submittal of the draft if NMFS
does not comment by then.
SOCAL
Comments and Responses
On October 14, 2008 (73 FR 60836), NMFS published a proposed rule
in response to the Navy's request to take marine mammals incidental to
military readiness training exercises in SOCAL and requested comments,
information and suggestions concerning the request. During the 30-day
public comment period, NMFS received 8 comments from private citizens,
comments from the Marine Mammal Commission (MMC) and several sets of
comments from non-governmental organizations, including, the Natural
Resources Defense Council (NRDC) (which commented on behalf of The
Humane Society of the United States, the International Fund for Animal
Welfare, Whale and Dolphin Conservation Society, Cetacean Society
International, Pamlico Tar River Foundation, League for Coastal
Protection, and Ocean Futures Society and its founder Jean-Michel
Cousteau), the Cascadia Research Collective (CRC), Ziphius EcoServices,
and Smultea Environmental Sciences, LLC. The comments are summarized
and sorted into general topic areas and are addressed below. Full
copies of the comment letters may be accessed at www.regulations.gov.
Monitoring and Reporting
Comment 1: One commenter stated that ``It is advisable to hold a
multi-day workshop to discuss controversial issues related to the
problem.'' The commenter further indicated that the workshop should
include representatives from the Navy, NMFS, relevant marine mammal
researchers, NGOs (e.g., NRDC), and invited experts on certain topics
of interest. The goal of the workshop should be to move towards
consensus on a way forward for the monitoring plan. Another commenter
suggested that outside expert review of the ICMP by professional marine
mammal biologists was needed.
Response: NMFS believes that a workshop consisting of the Navy,
NMFS, researchers, invited experts, and other interested parties, in
combination with an adaptive management plan that allows for
modification to the monitoring plan, would provide a means for the Navy
to potentially make changes to the Monitoring Plan that would more
effectively accomplish some of the goals of monitoring set forth
earlier in the Monitoring section. NMFS and the Navy have coordinated
on this point and the Navy will convene a workshop, to include (among
others) outside marine mammal experts, in 2011. The workshop and how it
will interact with the adaptive management component are discussed in
the Monitoring Workshop section of this final rule. The Monitoring
Workshop participants will be asked to submit individual
recommendations to the Navy and NMFS, and both agencies will work
together to determine whether modifications to the SOCAL Range Complex
monitoring are necessary based on the recommendations. As necessary,
NMFS would incorporate any changes into future LOAs and future rules.
However, NMFS disagrees with the commenter's suggestion that the
workshop participants seek to achieve consensus on a way forward for
the monitoring plan. NMFS has statutory responsibility to prescribe
regulations pertaining to monitoring and reporting, and will in
coordination with the Navy, develop the most effective and appropriate
monitoring and reporting protocols for future authorizations.
Comment 2: Two commenters made several recommendations regarding
the formatting and understandability of the monitoring plan, including
recommending additional text. For example, one commenter recommended
the Navy add a list of acronyms and another recommended adding text
explaining that dropping sonobuoys from monitoring observation aircraft
is another potential method of PAM whose feasibility and utility should
be assessed as part of the SCMP.
Response: NMFS and the Navy incorporated these recommendations
where appropriate. For example, both of the above examples were
incorporated. However, we did not incorporate the commenter's
recommendations in all cases, if we believed doing so, for example,
would needlessly lengthen and complicate the Plan or generally be
duplicative with the analytical contents of the rule.
Comment 3: One commenter stated: ``The Navy improperly assumes that
they have no impact on the marine mammals. It is clear that the draft
plan begins with the assumption that the Navy has no impact on marine
mammals, or that the current mitigation is adequate to eliminate
impacts. This is not supported by facts, and it invalidates the entire
purpose of the plan. The Navy must acknowledge that sonar testing may
indeed impact marine mammals and provide references, and must be
willing to work as an active partner in a plan to investigate the
extent and severity of such impacts, and how to reduce them to
insignificant levels. Otherwise, this entire exercise is just `window
dressing' and will be a major waste of taxpayer dollars.''
Response: NMFS disagrees with this commenter's assertion. It is
possible that the commenter mistook the fact that the Navy phrased some
of their goals as null hypotheses (``If marine mammals and
[[Page 3893]]
sea turtles are exposed to MFAS, what are their behavioral responses?
Are they different at various levels?'') to mean that they think there
are no effects. The Navy's LOA application and EIS clearly discuss the
potential adverse effects that marine mammals may experience when
exposed to MFAS/HFAS and explosive detonations. The Navy has and will
continue to work as an active partner to investigate the extent and
severity of the impacts and how to reduce them (see Navy Research
section of this final rule).
Regarding the issue of the mitigation being adequate to eliminate
impacts, nowhere does either the Navy or NMFS indicate that the current
mitigation will eliminate impacts. The MMPA requires that NMFS put
forth the means of effecting the least practicable adverse impacts. As
discussed in the Mitigation section of the proposed rule, NMFS has
determined that the final required mitigation accomplishes this. If it
were possible to eliminate impacts to marine mammals, an MMPA
authorization would not be necessary.
Comment 4: Two commenters were concerned that the Navy used the
term ``relative distance'' when describing the data that would be
gathered for marine mammals and sound sources and indicated that
precise measurements are needed to draw accurate conclusions.
Response: GPS measurements are used for the majority of Navy data,
both for ship tracks and marine mammal sightings. The word ``relative''
was used because in some cases the Navy cannot report exactly where
their exercise is for security reasons, but they can report exactly
where the marine mammal was relative to the sound source.
Comment 5: A few commenters asked why the Navy did not consider
additional survey methods, or modifications to the existing methods,
beyond those currently included in the plan, such as: dropping
sonobuoys from airplanes, specified focal follows of one animal before,
during, and after sonar; photo-identification of marine mammals to look
at residency patterns; or doing biopsy sampling to assess stress
hormones.
Response: There are many different methods available with which to
monitor marine mammals and the Navy considered a wide range of methods
in the development of their plan. NMFS considered all of the public
comments (including the recommended additional survey methods) received
during this rulemaking. Some of the methods suggested by the public,
such as the photo-identification method, would likely be feasible and
provide useful information (and in fact, the Navy will take photographs
whenever feasible), while other methods, such as biopsy sampling (which
would require a new research permit), would be more difficult both
financially and operationally. Nevertheless, the Navy must work within
the framework of the available resources and the operational
constraints associated with doing work in the vicinity of a complex
military exercise. NMFS provided input during the development of the
plan and believes that results from the required monitoring will
provide valuable information regarding the effects of MFAS on marine
mammals. Additionally, by including the Monitoring Plan as a
requirement of the regulations and LOA, NMFS is compliant with the MMPA
requirement to prescribe regulations setting forth the requirements
pertaining to the monitoring and reporting of taking. That being said,
the Navy and NMFS understand the importance of marine mammal monitoring
to determine the effects of MFAS, which is why the Navy agreed to
conduct the Workshop referred to in Comment 1 during which the
workshop participants will review and assess the monitoring results
(from this Monitoring Plan and others from other Range complexes and
areas) and make informed recommendations for how to move forward with
the best monitoring strategy.
Comment 6: One commenter asked that the Navy specify somewhere in
the Monitoring Plan that any potentially stranded animals will be
photographed for individual identification purposes.
Response: When possible, every attempt will be made to
opportunistically collect concurrent digital video and digital
photographs of animals under observation by both vessels and aircraft.
Direct experience with aerial monitoring within the Hawaii and SOCAL
Range Complexes in 2008 revealed the value of these techniques for on-
site and off-site species identification or confirmation, and for
assistance in reviewing a given animal's behavioral state after the
survey. Language to this effect has been added to the Monitoring Plan.
Comment 7: One commenter questioned who will conduct the Adaptive
Management Review and whether professional marine mammal and sea turtle
biologists will be involved as advisors on a regular basis.
Response: The NMFS and the Navy will conduct the Adaptive
Management Reassessment review to examine the prior year's monitoring
lessons learned, integrate new science, and re-direct monitoring based
on input from the scientific community. As mentioned in comment 1,
professional marine mammal biologists will be involved in the 2011
Monitoring Workshop.
Comment 8: One commenter noted that there is a lot of emphasis on
collection of data by Navy watchstanders, but the Navy must acknowledge
the limitation of these kinds of data. The relatively low level of
training and experience by these people (in relation to professional
marine mammal biologists) will make the data collected of little value.
Another commenter similarly notes that the marine species awareness
training consists primarily of watching a DVD, which is insufficient to
ensure that they accurately detect many species.
Response: Th